JOURNAL OF AGRICULTURAL SCIENCE IN FINLAND Maataloustieteellinen Aikakauskirja Vol. 58: 69—82, 1986 Flea beetles (Coleoptera, Chrysomelidae, Halticinae ) on rapeseed and sugarbeet in Finland ARJA AUGUSTIN, 1 UNTO TULISALO 1 and SEPPO KORPELA 2 1 Öljynpuristamo Oy, SF-00810 HELSINKI, Finland 2 Agricultural Research Centre, SF-13600 JOKIOINEN, Finland Abstract. Surveys of the incidence of flea beetles on sugarbeet and rapeseed were carried out in eight localities in southern and central Finland in 1972 and 1980—83. The first flea beetles emerged from overwintering in late April to early May, depending on the temperature. The majority, however, appeared during the second half of May, when daily temperatures oc- casionally reached +2O°C. Flea beetles found their host plants by olfactory orientation. Two population peaks occurred during the growing season. The overwintered flea beetles formed the first peak in late May to early June and the adults of the new generation the second peak starting in late July. The incidence of flea beetles fluctuated greatly on the cultivation, as the flea beetles moved only short distances and showed thus very local occurrence. The availabili- ty of host plants greatly affected their reproduction rate, and thus the annual and regional differences in the incidence of the flea beetles were great and depended solely on the availa- bility of host plants. Therefore it was difficult to establish any countrywide differences in the incidence of the beetles. Only Phyllolrela undulala (Kutsch.) and P. slriolala (F.) were of any importance as pests of rapeseed. P. undulala made up some 80—90 % and P. slriolala some 10 % of the total number of flea beetles on rapeseed. P. slriolala was more abundant on radish than on rapeseed. Sugarbeet was damaged only by Chaetocnema concinna (Marsh). Other species of flea beetles were also observed in small numbers on rapeseed, radish and sugarbeet. They did not, how- ever, cause any damage, but spread from adjacent cultivated plant species or weeds. The suc- tion trap collected only a few flea beetles, but clearly revealed their activity periods. Damage caused by flea beetles is most harmful during the short seedling stage. At that time one flea beetle per plant was considered the threshold level for control measures. Later, even several flea beetles did not significantly hamper the growth. Seed coating efficiently prevented damage by flea beetles. The general incidence of flea beetles observed during this study was so low that coating of the seed was not justified. Chemical control of blossom beetle efficiently reduced flea beetles as well. The abandoning of the cultivation of winter rape also reduced the total number of flea beetles. Index words: flea beetles, sugarbeet, rapeseed, control. 69 https://www.c-info.fi/en/info/?token=99lgSZznwLGz-D8O.fEyOQy0oibvA41R0Dw9FNQ.oFB6c_EEYeGooWBAj02PGg0erOtU7so3FO-isbfuEsg43ZdNXQWL8NdBhkAdhbDDUB14FE_IV-SDsnado6JNOPyIXECWqknD0zW0NKJM2UtHcAH1ytObz3-nD4jeqgAKdq_AF17nx3EXR66xvX5WkreBat-uZppQiPcZykaNO9WZkhPt4LqdukRFtIdux3YJCPp9elZfzTynOLkh 70 1. Introduction In Finland, 86 species of flea beetles (Cole- optera, Chrysomelidae, Halticinae) have been described (Silfverberg 1979). Most of the species live on native plants, although there are some harmful species, especially among Phyllotreta and Chaetocnema. Phyllotreta lives almost exclusively on plants belonging to the family of Cruciferae but also on closely related Äesecto-species and on Tropaeolum. Only Phyllotreta vittula (Redt.) lives on the family of Graminae (Heikertinger 1912, 1954, Freude et al. 1966). Chaetocnema lives primarily on plant species of Polygonaceae, Chenopodiaceae, Cyperaceae, Juncaceaeand Graminae (Heikertinger 1954). Of the nine Chaetocnema species found in Finland, four are considered to be pests, Chaetocnema con- cinna being the most harmful (Vappula 1962). The significance of flea beetles as perma- nent pests has been known for decades. The worst damage occurs early in the spring on cultivated Cruciferae and sugarbeet, when overwintered adults devour cotyledons. Tullgren (1929), Rostrup (1940), Muhlow and Sylven (1953), Vappula (1962) and Niel- sen (1977) and others have studied the distri- bution and biology of flea beetles in the Nor- dic countries. In general their global distribu- tion and biology are rather well known (e.g. Heikertinger 1912, 1954, Blunck 1921, Löttge 1955, Burgess 1977 and Sommer 1981). In Finland, the distribution of flea beet- les and their host plants have been studied by Poppius (1901), Linnaniemi (1916, 1920 a, 1920 b, 1935), Saalas (1933) and Vappula (1962). In spite of their annual occurrence and regular control, the quantitative relationships of flea beetle species and threshold levels have not yet been studied at any level. On the other hand, studies on the control methods have been numerous (e.g. Jameson 1958, Tiittanen & Varis 1960, 1961, 1963, Kinoshita et ai. 1978, Lamb 1984). The aim of this study is to explore the quan- titative relationships in the flea beetle fauna, their fluctuation within the growing season and from year to year as well as the damage caused by flea beetles, and the threshold levels for control measures. The ability of flea beetles to move to their host plants and other factors of orientation were also observed. 2. Material and methods Over 60 000 flea beetles were collected using different trapping methods in 1972 and 1980— 83. Most of the experiments were carried out at the Agricultural Research Centre in Van- taa. In 1983, flea beetles were also collected at eight localities in southern Finland. The species identification is based on the following works: Heikertinger (1912), Saalas (1933), Freude et al. (1966) and Keilbach (1966). Weather data are from the Kaisaniemi weather station in Helsinki. 2.1. Emergence of overwintered flea beetles and abundance and species composition on rapeseed, radish and sugarbeet Flea beetles were collected with Hardee " yellow bollweevil traps (Pest Management Specialists) and yellow and transparent pitfall traps. The traps were emptied daily or two to three times a week. The diameter of the pit- fall trap was 18 cm. The sweepnet was used later in the growing season. The net diameter was 30 cm and one sample consisted of 100 single sweeps. 2.2. Orientation of flea beetles Orientation of flea beetles to host plants was studied by placing greenhouse-reared young radish plants in 40 by 60 cm boxes out in the field at various distances from known overwintering sites in the beginning of the growing season. The boxes were placed in 12 sites, half of them on ploughed field and the other half on grass. Two boxes were placed five metres apart in each location, one with a transparent plastic cover. Flea beetles were trapped on a 20 by 20 cm glued transparent plate placed adjacent to each box and checked three times a week. The aim was to find out the role of odour and distance in the orienta- tion of flea beetles in the spring. 2.3. Use of suction trap A Johnson-Taylor suction trap (Johnson 1950) 1.2 m above ground level was used in 1981—82. In 1981 the trap was used from 9 May to 5 August and in 1982 from 11 May to 7 September. The number of flea beetles caught each day was recorded and the beetles identified by species. 2.4. Regional differences in flea beetlefauna and its abundance Flea beetles were collected with transparent pitfall traps at eight localities in South and Central Finland. At each locality five traps were placed in a rapeseed field of at least half a hectare in size. Flea beetles were caught for about one month in the beginning of the growing season. 2.5. Damage caused by flea beetles and threshold level for control measures The effect of flea beetles on the seed yield of rapeseed was studied in 1980 using cylin- der experiments. Four 10 by 10 m plots were sown on 16 May. The variety was »Torch» (untreated). Thirteen cylinders, each enclosing ten young rapeseed plants, were placed in each plot. Flea beetles collected from fields with the bollweevil traps were placed inside the cylin- ders in various numbers and intervals. From 2 to 9 June, 4 cylinders in each study plot con- tained 1, 2 and 3 flea beetles/plant and the control, and from 2 to 17 June, 2 to 21 June and 9 to 21 June respectively 1 and 2 flea beet- les/plant and the control. Rapeseed was at the seedling stage on June 2 and by June 9 young plants already had first pair of true leaves. After that the flea beetles and the cylinders were removed. The plants of the cylinder ex- periment were manually threshed when mature and seed yield determined. In 1982, twelve cages measuring 50 by 50 by 180 cm with metal frames and cheesecloth covering were laid in the field on June 4. In- side each cage there were 90 rapeseed seedlings. Flea beetles were collected from fields and re- leased inside the cages as follows: 100 in each of four cages, 50 in each of another four cages, and four cages formed a control group. Flea beetles were kept in these cages until June 13, when 20 seedlings from each cage were sampled and feeding signs counted. In 1981, in Vantaa, the rapeseed variety »Torch» was grown in two densities, 2.2 kg of seed/ha and 8 kg of seed/ha. Sowing day was May 18 and on June 8 ten plants were sampled from each of four replicates and the feeding signs counted. The plant density was counted on June 10 (based on 2x no. of plants/50 cm). Before harvesting, 20 plants from each replicate were collected. The length, diameter and the number of siliques on the main stem, the number of racemes and the number of siliques on them were measured. 2.6. Control experiments Control experiments were carried out in Vantaa in 1981—82 and in Jokioinen in 1983. In 1981, the experiment was established on May 18. The rapeseed variety was »Torch» and the fertilization level 100 kg N/ha. The harvested plot size was 12.0 m 2. The treat- ments were: E untreated, 8 kg of seed/ha F treated with isofenphos (30 g/kg of seed), 8 kg of seed/ha G untreated, 4.5 kg of seed/ha H untreated, 2.2 kg of seed/ha J pelletized seed, 8 kg of seed/ha. The feeding signs were sampled and counted on June 8. In 1982, the experiment was established on May 13—14, in the abovementioned way. The treatments were; A untreated, 12 kg of seed/ha 71 B treated with isofenphos (30 g/kg of seed) (treatment a), 12 kg of seed/ha C treated with hydroxyisoxazole (15 g/kg of seed), benomyl (2 g/kg of seed) and car- boxin (0,5 g/kg of seed) (treatment b), 12 kg of seed/ha G treatment b, 16 kg of seed/ha H untreated, 6 kg of seed/ha. The plant density counted on June 3 and on June 8 20 plants from each replicate were sampled and feeding signs counted. The control experiment in Jokioinen was sown on 23 May 1983. The variety was »Sigga» fertilized with 100 kg N/ha. The treatments were as in 1982. The plant density was recorded on June 6. Two weeks after the emergence, 20 plants from each replicate were sampled and flea beetle feeding signs were counted. In 1982, screening test for new prospective coating substances was conducted in Vantaa. The rapeseed variety was »Span» sown on May 24. There were seven coatings each with four replicates: A the untreated control B treated with isofenphos (40 g/kg of seed) C treated with isofenphos (20 g/kg of seed) D treated with captan (30 g/kg of seed) E treated with Kemira (experimental) no. 2 (30 g/kg of seed) F treated with Kemira (experimental) no. 5 (30 g/kg of seed) G treated with lindane (50 g/kg of seed) On June 2, flea beetle feeding signs were counted. The plant density was recorded on June 21. Flea beetles were also found in blossom beetle control experiments. These experiments were carried out in 1980 and in 1981 in Van- taa. The variety was »Torch» fertilized with 100 kg N/ha. The treated plots were sprayed twice with permethrin before flowering. In 1980, netting of beetles began on June 13. Samples consisting of 60 single sweeps were taken from both treated and untreated plots three times a week until August 18. In 1981, netting began on June 18 and samples were taken three times a week until August 6. Flea beetles were separated from the material, iden- tified by species and counted. 3. Results 3.1. Emergence of flea beetles from overwintering In 1982, the first overwintered flea beetles were observed as early as April 25. In the following year the first observations were two weeks later, on May 9. Thus the timeof emer- gence varied considerably. This was primari- ly due to the early spring weather, but ap- parently also to the location of the overwin- tering site. The majority of flea beetles, how- ever, emerged during the second half of May, whenboth day and night temperatures became markedly higher (Fig. I). 3.2. Orientation offlea beetles to host plants The orientation of flea beetles to host plants was observed by using young radish plants. These were placed out in the field well before the emergence of flea beetles and before the appearance of any green vegetation. The re- sults indicate that flea beetles were attracted by the odour of radish plants even to the bare, ploughed field (Fig. 2). Visual orientation Fig. I. Numbers of flea beetles caught with 10 yellow pitfall traps placed on grass from 24 April to 1 June 1982 and maximum daily temperatures in Vantaa. 72 seemed to be of little importance, for clearly visible but covered radish plants attracted few flea beetles. Flea beetles became active when daytime temperatures exceeded + 15°C while extended movement occurred at temperatures above +2O°C. These experiments also indi- cated that flea beetles move rather short distances i.e. only a few hundred metres. When the food supply is near, the movement is reduced to less than a hundred metres. This is supported by the observation that, in the autumn, flea beetles remained on host plants until late retirement to overwintering sites in October, while some even overwintered in winter turnip rape fields. Radish plants attracted especially Phyllotreta undulata and P. striolata, which live on Cruciferae-species, but other species were represented by only a few randomly caught specimens. 3.3. Suction trap observations Compared with other collecting methods, the suction trap observations (Fig. 3) quite clearly indicated the appearance and activity period of flea beetles during the growing season. On the other hand, the rather low numbers indicated that flea beetles move close to the ground and only short distances. They did not even reach the one metre height re- Fig. 2. Numbers of flea beetles caught on radish boxes from 10 May to 2 June 1982 in Vantaa Fig. 3. Daily yields of suction trap and the maximum temperatures in Vantaa from 9 May to 8 August 1981 73 quired for effective trap function. The annual variation in the numbers of trapped flea beetles was apparently the result of differ- ences in the cultivation pattern. In 1981 there was still a rather large area of rapeseed in the vicinity of the trap, whereas in 1982 the adja- cent plot was only about 10ares and the larger field was several hundred metres away. The importance of temperature in controlling flea beetle activity was further supported by the trap observations. Numbers were abundant only when the daytime temperature exceeded -i-20°C. In 1982, there was a ten day cold period in May. The daytime temperature was only about -I- 12°C and no flea beetles were found in the suction trap. 3.4. Species composition In spring, before the growing season, traps placed on grass and ploughed field collected several species of flea beetles (Table /.). At this time flea beetles were moving in the vicin- ity of overwintering sites searching for suitable host plants. The species found on young sugarbeet plants in 1981—83 are shown in Table I. The numbers of flea beetles were always very low, and the percentage distribution thus gives a distorted impression of the importance of dif- ferent species. The abundance of Chaetocnema concinna varied greatly. The species composition was strongly affected by the influx of flea beetles from the adjacent vegetation. In 1981 the sugarbeet field was surrounded by barley fields and Phyllotreta vittula was abundant on sugarbeet. In 1982, P. undulala and P. strio- lata, typical species on Cruciferae plants, in- vaded sugarbeet from the large rapeseed field nearby. The Longitarsus sp. moved to sugar- beet from weeds. In 1983, the sugarbeet plot of 1 are was surrounded by rapeseed and radish plots of the same size and the propor- tion of Chaetocnema concinna remained small. Phyllotreta undulala was the dominant spe- cies on young rapeseed plants (Table 1). Its proportion varied from 75 % to 85 %. In 1981, the rapeseed plot was in the middle of a barley field, which explains the proportion of P. vittula. The abundance of P. slriolala varied from 3 % to almost 9 %. Of other spe- cies only a few specimens were found and they were thus insignificant as pests. Young radish plants attracted flea beetles quite effectively ( Table I). The species com- position and relative abundance were of similar type as described for rapeseed. How- ever, the proportion of P. slriolalawas greater than on rapeseed, being from 14 % to 24 %. The species composition in the sweepnet Table 1. Species composition of flea beetles on grass and ploughed field, sugarbeet, rapeseed and radish in spring 1981—83 in terms of percentage of the total number of beetles. Grass and Sugarbeet Rapeseed Radish ploughed field ]9gl 1982 19g3 1981 1982 i 983 1982 1983 Chaetocnema aridula 4.8 0.4 C. concinna 18.9 76.3 28.6 11.3 2.7 4.0 0.2 0.7 1.4 C. hortensis 3.5 0.8 15.3 0.5 3.3 0.3 0.8 C. mannerheimi 11.4 1.8 2.8 1.6 2.5 Longitarsus sp. 7.2 1.8 12.5 2.5 4.1 0.5 Phyllotrela armoraciae 0.5 P. atra 0.2 0.3 0.1 P. flexuosa 2.1 1.2 P. nemorum 0.2 0.4 P. striolata 3.4 0.9 8.1 23.4 3.3 6.3 8.8 24.4 13.5 P. undulala 22.3 7.0 44.8 42.7 73.9 84.3 85.1 73.6 82.1 P. vittula 32.9 12.3 2.4 0.8 14.3 0.3 0.2 0.5 0.4 Total no. flea beetles 2591 114 248 124 384 800 422 2529 513 74 3 Table 2. Species composition of flea beetles in sweepnet samples collected in Isokyrö in 1972 and in Vantaa in 1980—83 in terms of percentage of the total number of beetles. Vantaa Isokyrö 1972 Rapeseed Radish Sugarbeet 1983 1983 Swede Turnip 1980 1981 1982 1983 rape rape Chaetocnema aridula C. concinna 0.7 1.9 0.3 0.3 0.4 0.5 30.5 C. hortensis 0.1 C. mannerheimi Longitarsus sp. 0.5 2.0 Phyllolrela armoraciae P. atra 0.2 P. flexuosa P. nemorum 1.3 P. striolata 26.1 43.4 6.4 1.6 6.5 33.8 63.2 63.0 P. undulata 73.7 55.9 89.1 97.2 92.7 65.0 34.4 4.5 P. vitlula 2.7 0.9 0.3 0.1 0.4 Total no. flea beetles 1704 4952 36558 958 789 786 2305 246 samples is presented in Table 2. The samples from Isokyrö are interesting because rapeseed and sugarbeet had not been cultivated in the region for ten years before the sampling. Thus the species composition to a great extent re- presents the natural flea beetle fauna of the region. The results of the 1981—82 netting from rapeseed indicate that the proportion of P. undulata in the new generation continued to increase. Table 2 shows how P. striolata favoured radish. It also dispersed to rapeseed and sugarbeet, whereas Chaetocnemaconcin- na moved to neither rapeseed nor radish. 3.5. Abundance offlea beetles During the growing season two peaks of abundance occurred (Fig. 4). The first peak in May-June consisted of overwintered flea beetles and the other in July-August of adults of the new generation. The incidence of flea beetles varied greatly also from year to year. The incidence of flea beetles on the experiment area in Vantaa seemed to decrease with a decrease in the cultivation area of rapeseed and sugarbeet. In 1979—80, there was still a 0.5 hectare plot of winter turnip rape on which flea beetles thrived. Later in summer great numbers of flea beetles of the new generation moved to spring turnip rape nearby. In 1980— 81, spring turnip rape was treated against blossom beetles and that reduced also flea beetle numbers effectively (Table 3). Fig. 4. Numbers of flea beetles collected on rapeseed with 18 transparent pitfall traps (27. 5.—7. 6.) and sweepnet (21. 6.—1. 9.) and the maximum daily temperatures in 1982 in Vantaa. 75 Table 3. Numbers of flea beetles in sweepnet samples collected from the blossom beetle control experiments in 1980 (two fields, I and II) and 1981 (field I). 1980, 1 1980, II 1981, I 13. 6.—18. 8.13. 6.—18.8.18. 6.-6. 8. Treated plot (A) 20 210 236 431 Control plot (B) 36 558 377 958 A:B (%) 55.362.6 45.0 Table 4. Species composition of flea beetles collected with five transparent pitfall traps on rapeseed at seven experimental stations in terms of percentage of the total number of beetles. Agric. Res. Satakunta South-west Central South Savo Kymenlaakso Porvoo Centre exp. sta. exp. sta. Finland exp. sta. exp. sta. commune Jokioinen exp. sta. Chaelocnema aridula C. condnna 3.92.9 13.3 9.21.1 25.3 C. hortensis 0.8 5.95.6 C. mannerheimi 0.723.3 1.2 4.0 Longitarsus sp. 0.7 1.20.8 6.75.6 Phyllotreta armoraciae P. atra P. flexuosa 0.1 _ P. nemorum 0.5 P. striolata 17.98.0 17.712.6 1.13.5 P. undulata 71.787.7 50.080.0 71.491.1 54.0 P. vittula 5.4 13.3 1.5 Total no. flea beetles 736 260 119 260 119 90 198 3.6. Regional species composition and abundance of flea beetles The species composition of flea beetles col- lected at various experimental stations is presented in Table 4. Phyllotreta undulata was the dominant species in all regions, its rela- tive abundance varying from 50 % (SW-Fin- land Exp.Sta.) to 91 % (Kymenlaakso Exp. Sta.). P. striolata was the second most com- mon species and its proportion seemed to increase northwards. In Porvoo commune, sugarbeet was grown near the rapeseed field, which explains the abundance of Chaetocne- ma concinna. Conclusions about the regional abundance cannot be made from these results because flea beetles are rather local in occur- rence. For example, the numbers of flea beetles were low at the Southwest Finland Exp. Station although Cruciferae plant spe- cies have been cultivated there for several years. 3.7. Damage and threshold levels for control The damage caused by flea beetles and its impact on yield were studied in cylinder and cage experiments. The results are presented in Fig. 5 and Table 5. It seems that in the average growing conditions one flea beetle per coty- ledon is the threshold level for control mea- sures. However, damage is greatly affected by the growing conditions. Serious damage oc- curred only during the relatively short seed- ling stage. Later, even numerous flea beetles did not hamper the growth of host plants. The rather high plant density, 350 plants/nT, is a good protection against damage, for in the usual growing conditions the threshold level of 76 77 Table 5. Effect of flea beetles on the seed yield of rapeseed in the cylinder experiments in 1980 in Vantaa. Period Control Seed yield, g/10 plants 1 beetle/plant 2 beetles/plant 3 beetles/plant 2. 6.—9. 6. 7.90±2.59 3.43±1.24 2.51 ± 1.53 1.65±0.49 2. 6.—17. 6. 5.90± 1.59 2.48+0.59 1.40± 1-16 9. 6.—21.6. 6.43±1.40 8.24±2.62 7.27±2.86 ■■ one flea beetle per cotyledon is very seldom reached. On the other hand, rapeseed is capable of efficiently compensating for early thinning of the plant stand (Table 6). growing conditions were better. During con- trol experiments flea beetles did not occur in numbers that would require routine coating of the seed. On the other hand, as Table 3 shows, the control of blossom beetles in about mid-June reduced the numbers of flea beetles too. 3.8. Control measures For decades flea beetles have been con- trolled by routinely coating the seed. In the experiment carried out in 1980—83 it was found that the products used protected the co- tyledons as expected (Tables 7 to 9). Of the new products, captan was found to be as ef- fective as isofenphos, which was rather effec- tive also in low dosage. When the results of 1982 and 1983 are compared, the effects of the growing conditions upon the emergence and the compensation capability of rapeseed and the amount of damage are all clearly ob- servable. In the average growing conditions of 1982 the effect of the coating was positive, but its significance decreased in 1983 when the Table 6. Comparison of the sparse seedling (2.2 kg/ha) and the dense seedling (8 kg/ha) of rapeseed in Vantaa in 1981. Sparse seedling Dense seedling (x ± s) (x ± s) Plants/50 cm 7.5 ±0.6 17.6±3.8 Feeding signs/plant 12.5± 2.7 12.3± 4.4 The main stem Length (cm) 99.3 ±5.6 99.5 ±B.O Siliques 13.4±3.4 21.5±6.9 Diameter of the main stem (mm) 6.6± 1.1 5.6±0.8 Racemes 3.5 ±0.4 2.8 ±0.4 Siliques on the racemes 76.0± 19.9 38.6±8,6 The yield (kg/ha) 1076.3 ±33.7 1200.0 + 28.3 Table 7. Flea beetle feeding signs on rapeseed coated with various substances in Vantaa 1982. Treatment Plants/50 cm Feeding signs/plant A = the control B = isofenphos, 40 g/kg seed C = isofenphos, 20 g/kg seed D = captan, 30 g/kg seed E = Kemira exp. 2, 30 g/kg seed F = Kemira exp.s, 30 g/kg seed G = lindan, 50 g/kg seed 16.4 a 8.9 a* 19.6 a 3.1 b 20.3 a 2.8 b 17.5 a 2.1 b 18.9 a 7.0 a 17.3 a 5.5 ab 20.6 a 2.5 b * Tukey’s t-test Fig. 5. The feeding signs/plant in cages containing various numbers of flea beetles in the cage ex- periment in 1982 in Vantaa. 4. Discussion Flea beetles become active and emerge from overwintering sites when temperatures rise in spring. In southern Finland a few flea beetles can be found at the end of April, but most of them appear during the last third of May when night and daytime temperatures usual- ly rise significantly. The emergence is affected by the temperature close to the ground. On sunny spring days this is often higher than the temperature two metres above the ground. Flea beetles also emerge earlier from sunny sites than from shaded ones (Löttge 1955). No clear differences in the timing of emergen- ce were observed between the species. Infor- mation in the literature is conflicting (e.g. Muhlow& Sylven 1953, Löttge 1955, Jones & Jones 1974), but Sommer (1981) too states that there are no clearly observable differences in the emergence of different species. The lowest temperature in which Burgess (1977) observed flying flea beetles was + 14—15°C. According to Blunck (1921) and Löttge (1955) the temperature must be at least + 18°C before flea beetles fly from overwintering sites to host plants. According to Jones& Jones (1974) this dispersal flight does not begin before the daytime tempera- ture reaches +2O°C. The suction trap obser- vations and the radish box experiments indi- cate that flea beetles fly longer distances only after the daytime temperature reaches about + 20°C. However, flea beetles did also fly at lower temperatures than the +lB°C men- Table 8. The flea beetle control experiment in Vantaa 1981. Treatment Plants/50 cm Feeding signs/plant Yield (kg/ha) E = untreated, 8 kg of seed/ha F = isofenphos (30 g/kg of seed), 8 kg of seed/ha G = untreated, 4.5 kg of seed/ha H = untreated, 2.2 kg of seed/ha J = pelletized seed, 8 kg of seed/ha 17.6 a 12.3 a 17.5 a 9.2 a 9.4 b 14.4 a 7.5 b 12.5 a 22.5 a 8.3 a 1200 a* 1364 a 1245 a 1076 ab 1369 a * Tukey’s t-test Table 9. Flea beetle control experiments in Vantaa 1982 and in Jokioinen 1983. Treatment Plants/50 cm Feeding signs/plant 1982 1983 1982 1983 20.1 a 20.6 a 12.3 a 3.9 a 24.7 b 26.3 a 9.2 a 1.9 b 19.3 a 18.5 ab 12.0 a 2.5 ab 25.9 b 26.8 a 12.8 a 2.3 b 14.4 c 10.3 c 15.1 a 4.7 a Yield (kg/ha) 1982 1983 1613 a 1915 a* A = untreated, 12 kg of seed/ha B = treatment a, 12 kg of seed/ha 1650 a 1932 a C = treatment b, 12 kg of seed/ha 1674 a 1950 a G = treatment b, 16 kg of seed/ha 1686 a 1951 a H = untreated, 6 kg of seed/ha 1422 a 2056 a treatment a = isofenphos (30 g/kg of seed) treatment b = hydroxyisoxazole (15 g/kg of seed), benomyl (2 g/kg of seed), and carboxin (0.5 g/kg of seed) • Turkey’s t-test 78 tioned by Blunck (1921) and Löttge (1955). For instance, the lowest daytime temperature at which the suction trap caught flea beetles was + 13.5°C. The trap catches insects at a height of I—21 —2 m in the air (Johnson 1950), and the flea beetles caught were thus apparent- ly on an extended flight. The suction trap observations quite clearly indicate the timing of emergence and the mobility of flea beetles during the growing season. According to Sommer (1981) the availabil- ity of host plants in spring greatly affects the development of flea beetle populations. This was also clearly observed in summer 1980 in Vantaa. The winter turnip rape field provided an ample food supply for flea beetles in spring. They reproduced extremely well, and the new generation moved in masses to feed on the adjacent spring rape field. The culti- vation of winter turnip rape ceased in Finland in the mid 19705, which to some extent at least has evidently kept flea beetle populations rather low recently. According to Moreton (1945) flea beetles disperse randomly during favourable weather conditions and are not attracted by Cruciferae- species. Numerous other studies indicate, however, that flea beetles find their Cruciferae host plants by olfactory orientation. Mustard oils and mustard oil glucosides function as at- tractants (Görnitz 1953, 1956, Feeny et al. 1970, Hicks 1974, Nielsen 1977). In addition, initiation of feeding is affected by feeding in- hibitors these plants contain, such as glucosi- nolates and flavonoids (Nielsen et al. 1977, Nielsen 1978, Vargas& Kershaw 1979). The radish box experiments also clearly indicated that flea beetles are attracted to their host plants by odour cues. Radish attracted only Phyllotreta undulata and P. striolata, which feed on Cruciferae species. Of other species, only a few beetles were caught, as also on the covered radish boxes. The flea beetle species on cultivated plants in Finland have been studied by a few authors, such as Linnaniemi (1920 b, 1935), Saalas (1933) and Vappula (1962). According to Vappula (1962), of the flea beetles found on Cruciferae-species, Phyllotreta undulata is especially harmful, P. atra, P. nemorum (L.) and P. striolata being quite harmful. Chae- tocnema concinna is especially harmful on beets. The experiments in 1972 and 1980—83 indicate, however, that only P. undulata and P. striolata had any significance as pests of Cruciferae-species. Chaetocnema concinna is the only flea beetle species damaging sugar- beet in Finland. During this study it was rather rare, but on extensive sugarbeet fields it may increse rapidly. Flea beetles normally living on other cultivated plant species or weeds moved also to rapeseed, radish and sugarbeet, but they did not cause damage. No clear differences between the species composition were observed in southern and central Finland. P. undulata was the most common species, P. striolata being the second. The relative abundance of P. striolata in- creased somewhat towards the north. The surrounding vegetation greatly affected the species composition at all collection sites. It is not possible to estimate the regional in- cidences of flea beetles for the numbers may vary greatly even within a small area. Con- tinuous cultivationof suitable host plants will increase the abundance of flea beetles. In Southern Finland the spring peak in- cidence was reached in May-June while the new generation appeared in July-August depending on the weather. In Finland flea beetles have only one generation per year. In Central Europe the peaks are reached earlier than in Finland, and at least P. undulata has been observed to have a second generation (Löttge 1955, Jourdheuil 1960, Sommer 1981). Flea beetle numbers also fluctuate annually, depending, for instance, on weather conditions in the growing season and the availability of host plants (Sommer 1981). The incidence may vary considerably even within a small area and even the polyphagous Phyllotreta species prefer some host plants to others (Haddock 1945, Dobson 1956, Sommer 1981). The cylinder experiments clearly indicated that the relatively short seedling stage (about 79 one week after germination) is the most sen- sitive period to flea beetle damage. Later, even several flea beetles did not hamper the growth. This is mentioned by Taylor (1968) and Lamb (1984), too. According to Lamb (1984) damage was most significant during the first weeks after germination. During the first week the seedling mortality was high and the growth was slow during the first couple of weeks. The spring weather also affects the magnitude of damage (Löttge 1955, Sommer 1981). Ac- cording to Lebedev (1924) and Pimentel (1961) flea beetles are more numerous in sparse than in dense growth. In the present study the numbers of flea beetles per sq.metre were so low that no difference in damage was observed between the sparse and dense growths. The sowing density of rapeseed, 350 seedlings/m 2 , provides a good protection against damage. Rapeseed is also able to com- pensate for the seedling loss by branching. For decades seeds have been coated to prevent damage by flea beetles. These experi- ments indicated that the products now in general use reduce flea beetle damage effec- tively. Spraying against blossom beetles effec- tively reduced the numbers of flea beetles as well. 5. Literature Blunck, H. 1921. Erdflohkäfer an den ölsaaten im Jahre 1920. Arbeiten aus der Biol. Reichsanstalt 10: 406—466. Berlin. Burgess, L. 1977. Flea beetles (Coleoptera: Chrysome- lidae) attacking rape crops in the Canadian provinces. Can. Ent. 109: 21—32. Dobson, R.M, 1956. A note on the relative abundance of flea beetles (Phyllolrela Stephens and Psylliodes Berthold) on different cruciferous crops. J. Hort. Sci. 31: 291—294. Feeny, P., Paauwe, K.L. & Demong, N.J. 1970. Flea beetles and mustard oils: host plant specificity of Phyl- lolrela cruciferae and P. slriolala adults (Coleoptera: Chrysomelidae). Ann. Em. Soc. Am. 63: 832—841. Freude, H., Harde, K.W. & Lohse, G.A. 1966, Die Käfer Mitteleuropas. Part 9. Cerambycidae, Chrysome- lidae. 299 p. Krefeld. Görnitz, K. 1956. Untersuchungen fiber in Cruciferen enthaltene Insekten-Attraktivstoffe. Nachr.bl, dt, Pfl.schutzd. N.F. 7: 81—95. Haddock, M.J. 1945. Observations on the species of flea beetles infesting Brassica crops in the west of England. Ann. Rep. Long Ashton Res. Sta. for 1944: 166—169. Heikertinger, F. 1912. Halticinae. Fauna Germanica; Die Käfer des Deutchen Reiches. Part IV. p. 143—212. Stuttgart. —, 1954. Halticinae. Handbuch der Pflanzenkrankhei- ten. Part V. Berlin and Hamburg. Hicks, K.L. 1974. Mustard oil glucosides: feeding stimu- lants for adult cabbage flea beetles Phyllolrela cruci- ferae (Coleoptera, Chrysomelidae). Ann. Em. Soc. Am. 67: 261—264. Jameson, H.R. 1958. The mechanism of control of tur- nip flea beetle by benzene hexachloride dressings on brassica seeds. J. Sci. Food Agric. 9: 590, Johnson, C.G. 1950. A suction trap for small airborne insects which automatically segregates the catch into successive hourly samples. Ann. Appi. Biol. 37: 80—91. Jones, F.G. & Jones, M.G. 1974. Pests of field crops. Second edition. 448 p. New York. Jourdheuil, P, 1960. Remarques sur le nombre de gen- erations de quelques Phyllolrela (Col., Chrysomelidae). Bull. Soc. Ent. Fr. 65: 126—131. Keilbach, R. 1966. Die tierischen Schädlinge Mittel- europas. 784 p. Jena. Kinoshita, G.8., Svec, H.J. & Mceven, F.L. 1978. Lab- oratory and field studies on the chemical control of the crucifer flea beetle, Phyllolrela cruciferae (Coleoptera, Chrysomelidae), on cruciferous crops in Ontario. Can. Em. 110: 795—803. Lamb, R.J. 1984. Effects of flea beetles, Phyllolrela spp. (Coleoptera, Chrysomelidae), on the survival, growth, seed yield and quality of canola, rape and yellow mustard. Can. Em. 116: 269—280. Lebedev, V.A. 1924. [On the means for combating garden insects of the genus Phyllolrela, and on the effect of these on the growth and yields of plants]. Zashch. Rast. 1; 131 138. In Russian, translation E. Matthews. Linnaniemi, W.M. 1916. 20. kertomus tuhohyönteisten esiintymisestä Suomessa vuonna 1914. Maanviljelyhän. Tied. 111. 75 p. —, 1920 a. Sokerijuurikasviljelyksen tuhohyönteiset ja niiden torjumiskeinot. 71 p. Helsinki. —, 1920 b. 20—21 (21 —22) kertomus tuhoeläinten esiin- tymisestä Suomessa vuosina 1915 ja 1916. Maatal,hali. Tied. 131. 132 p. —, 1935.23. kertomus tuhoeläimen esiintymisestä Suo- messa vuosina 1917—1923. Valt, Maatal. Koetoim. Julk. 68. 159 p. 80 Löttoe, W. 1955. Möglichkeiten einer Prognose bei Gemiiseschädlingen erörtert am Beispiel der Kohlerd- flöhe (Phyllolrela). Kuhn-Arch, 69: 493—551. Moreton, B.D. 1945. On the migration of flea beetles (Phyllolrela spp.) (Coleoptera, Chrysomelidae) attack- ing Brassica crops. Ent. Month. Mag. 81: 59—60. Ser. 4. London. Muhlow, J. & Sylven, E. 1953, Oljeväxternas skadedjur. Natur och Kultur. 163 p. Stockholm. Nielsen, J.K. 1977. Host plant relationships of Phyl- lolrela nemorum L. (Coleoptera: Chrysomelidae). I. Field studies. Z. Ang. Ent. 84: 396—407. —, Larsen, L.M. & Sorensen, H. 1977. Cucurbitacin E and 1 in Iberis amara: feeding inhibitors for Phyllolrela nemorum. Phytochemistry 16: 1519—1522. Pimentel, D. 1961. The influence of plant spatial pat- terns on insect populations. Ann. Ent. Soc. Amer. 54: 61—69. Poppius, B. 1901 . Über die Entwickelung von Phyllolrela armoraciae Koch. Medd. Soc. Fauna et Flora Fenn. 27: 106—111. Rostrup, S. 1940, Vort Landbrugs Skadedyr. 400 p. Copenhagen. Saalas, U. 1933. Viljelykasvien tuho- ja hyötyhyöntei- set sekä muut selkärangattomat eläimet. 676 p. Por- voo. Silfverberg, H. 1979. Enumeratio Coleopterum Fenno- scandiae et Daniae. Helsingin hyönteisvaihtoyhdistys. Helsinki. Sommer, G. 1981. Biologie und Parasitenkomplex der Halticinen Gattung Phyllolrela. 317 p. Taylor, W.E. 1968. The effects of leaf eating insects, especially Plulella maculipennis Curtis and Phaedon cochleriae F. on the growth and yield of some cruci- ferous plants. Ph. D. Thesis, University of London. Tiittanen, K. & Varis, A.—L. 1960. The treatment of seeds of swede, turnip and turnip rape in the control of flea beetles (Phyllolrela spp.) and cabbage root flies (Hylemyia brassicae Bouche and H. JloralisFall.). Valt. Maatalouskoetoim. Julk. 181: I—ll. —, & Varis, A.-L. 1961. Ristikukkaisten rehukasvien siementen lindaanikäsittely kaalikärpästen jakirppu- jen torjunnassa. Maatal. ja Koetoim. 15: 264—274. —, & Varis, A.-L. 1963. The effect of storage on the germination of lindane treated seeds and on the effi- cacy of such treatment in controlling flea beetles (Phyl- lolrela spp.) and cabbage root flies (Hylemyia spp.). Ann. Agile. Fenn 2: 44—50. Tullgren, A. 1929. Kulturväxterna och djurvärlden. 387 p. Stockholm. Vappula, N.A. 1962. Suomen viljelykasvien tuhoeläin- lajisto. 275 p. Helsinki. Vargas, P. & Kershaw, W.J.S. 1979. Host selection and choice of feeding site by the flea beetle Phyllolrela undulata Kutsch. Anales del Institute Nacional de In- vestigaciones Agraria. Proteccion Vegetal 10: 81 —93. Ms received May 30, 1986 SELOSTUS Kirpat (Coleoptera, Chrysomelidae, Halticinae) rypsi- ja sokerijuurikasviljelyksillä Arja Augustin, 1 Unto Tulisalo 1 ja Seppo Korpela 2 1 Öljynpuristamo Oy, SF-00810 Helsinki, Finland 2 AgriculturalResearch Centre, SF-13600 Jokioinen, Finland Maatalouden tutkimuskeskuksessa Vantaalla sekä seit- semällä muulla paikkakunnalla Etelä- jaKeski-Suomessa selvitettiin vuosina 1972 ja 1980—83 kirppojen esiinty- mistä rypsi- ja sokerijuurikasviljelyksillä. Etelä-Suomessa ensimmäiset kirpat lähtivät liikkeelle talvehtimispaikois- taan lämpötilan mukaan huhti- ja toukokuun vaihtees- sa. Suurin osa kirpoista ilmestyi kuitenkin toukokuun lop- pupuoliskolla, kun päivälämpötilat ajoittain kohosivat 20°C:seen. Kirpat suunnistivat ja löysivät isäntäkasvin- sa hajun perusteella. Kasvukauden aikana oli kaksi run- saushuippua. Ensimmäisen muodostivat talvehtineet yk- silöt touko- ja kesäkuun vaihteessa ja toisen uuden su- kupolven aikuiset heinäkuun lopussa. Kirppojen esiinty- misrunsaus viljelyksillä vaihteli paljon, sillä kirpat liik- kuivat vain lyhyitä matkoja; täten niiden esiintyminen oli hyvin paikallista. Isot vuotuiset runsausvaihtelut johtui- vat lähinnä isäntäkasvitilanteen muutoksista. Tämän vuoksi oli vaikeata nähdä, vaihteliko kirppojen esiinty- misrunsaus alueittain. Ainoastaan Phyllolrela undulata (Kutsch.) jaP. strio- 81 lata (F.) olivat merkittäviä tuholaisia rypsiviljelyksillä. P. undulala.n osuus oli 80—90 % jaP. slriolala:n n. 10 % kirppojen kokonaismäärästä. P. slriolala oli yleisempi retiisi- kuin rypsiviljelyksillä. Sokerijuurikasta vioitti ainoastaan Chaetocnema concinna (Marsh). Myös mui- ta kirppalajeja esiintyi vähäisinä määrinä rypsi-, retiisi- ja sokerijuurikasmailla. Nämä eivät kuitenkaan aiheut- taneet tuhoja. Imupyydys keräsi vähän kirppoja, mutta se osoitti silti selvästi kirppojen esiintymisajankohdat. Kirpat aiheuttivat eniten vahinkoa lyhyen sirkkataimi- vaiheen aikana. Torjunnan kynnysarvo oli tuolloin yksi kirppa/kasvi. Myöhemmin useatkaan kirpat eivät enää estäneet kasvua. Kirppojen esiintymisrunsaus oli tutki- muksen aikana niin pieni, että siementen torjunta-aine- kuorrutus oli tarpeeton. Syysrypsin viljelyn loppuminen näytti olevan osasyynä kirppojen vähäiseen määrään. Toi- saalta tuholaistorjunta rapsikuoriaista vastaan tehoaa myös kirppoihin. 82