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Article

Side Effects of Kaolin and Bunch-Zone Leaf Removal on Generalist Predators in Vineyards

by
Elena Cargnus
,
Federico Tacoli
,
Francesco Boscutti
,
Pietro Zandigiacomo
and
Francesco Pavan
*
Department of Agricultural, Food, Environmental and Animal Sciences, University of Udine, Via delle Scienze 206, 31000 Udine, Italy
*
Author to whom correspondence should be addressed.
Insects 2023, 14(2), 126; https://doi.org/10.3390/insects14020126
Submission received: 9 December 2022 / Revised: 14 January 2023 / Accepted: 20 January 2023 / Published: 25 January 2023
(This article belongs to the Special Issue Diversity and Abundance of Predators and Parasitoids of Insect Pests)
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Abstract

:

Simple Summary

Kaolin application and bunch-zone leaf removal are two cultural practices that contribute to the control of main pests in vineyards, such as leafhoppers and the European grapevine moth. In the context of Integrated Pest Management (IPM), a two-year study on the side effects of these practices on generalist predators was conducted in three vineyards of a grape-growing area in north-eastern Italy. This study provides the first data on the influence of kaolin and bunch-zone leaf removal on spiders and predatory insects occurring in vineyards. It was demonstrated that moderate use of kaolin has a negligible impact on generalist predatory arthropods in vineyards, while no negative effects were associated with bunch-zone leaf removal. Therefore, these practices were compatible with IPM strategies.

Abstract

In vineyards, kaolin application and bunch-zone leaf removal (LR) were effective in the control of leafhoppers and Lobesia botrana, but their side effects on generalist predators are still poorly understood. In north-eastern Italian vineyards, the impact of kaolin and LR on species and functional diversity of spiders, as well as the abundance of spiders and generalist predatory insects, was assessed in one vineyard for two consecutive years and in two vineyards for one year. The ecological indices of the spider community were never influenced by kaolin and only in one case were they influenced by LR. At the spider family level, kaolin reduced the abundance of Araneidae, Oxypidae and Salticidae, but only in single cases. In single cases, kaolin reduced the amount of Orius sp. anthocorids and increased that of Scymninae coccinellids, whereas LR increased the amount of Aeolothrips sp. The moderate use of kaolin and the application of LR had negligible and inconsistent impacts on generalist predatory arthropods in vineyards and were therefore, compatible with IPM strategies.

1. Introduction

Plants sprayed with kaolin, a white aluminum silicate, become visually, tactually and chemically unrecognizable to arthropod pests [1]. The treated substrates impaired the adhesion of a Pentatomidae bug and a Tephritidae fly due to particles of kaolin sticking to their legs [2]. Pests can be negatively affected by kaolin mostly by reducing egg laying and feeding activity [3]. Its applications were effective in pest control in orchards and field crops [4,5,6,7,8].
In vineyards, kaolin was effective against sap-sucking pests, such as the leafhoppers Hebata vitis (Göthe) [9] [syn. Empoasca vitis (Göthe)], Zygina rhamni Ferrari, Arboridia kermanshah Dlabola, Erasmoneura vulnerata (Fitch) and Scaphoideus titanus Ball [10,11,12,13], the grape phylloxera Daktulosphaira vitifoliae (Fitch) [14] and the vine cicada Psalmocharias alhageos [15], as well as carpophagous pests, such as the European grapevine moth Lobesia botrana (Denis and Schiffermüller) [16,17] and the spotted wing drosophila Drosophila suzukii Matsumura [18]. Kaolin provided an effective control of two polyphagous scarab beetles Macrodactylus subspinosus (Fabricius) and Popillia japonica Newman, feeding on grapevine leaves and bunches [19,20].
Bunch-zone leaf removal is a common cultural practice in vineyards, which consists of removing all the leaves that cover bunches, contributing to the control of both bunch rots and L. botrana [21,22]. Larvae of the carpophagous generations can die just after hatching due to high temperatures recorded on the sun-exposed berries where eggs were laid [23]. The combination of kaolin with bunch-zone leaf removal provides synergistic control of L. botrana with the added benefit that kaolin reduces sunburn damage to the berries often caused by sun exposure of bunches [17,24].
In the context of Integrated Pest Management (IPM), kaolin and bunch-zone leaf removal can be considered a valid alternative to synthetic insecticides only if their side effects on natural enemies are comparably less negative and not such as to favour the resurgence of pests. In fact, spiders and generalist predatory insects can have a significant impact on pest populations in several agro-ecosystems [25,26,27]. The ability to feed on alternative prey allows generalists to also be present inside a crop when pest population densities are still low, and they may delay or prevent pest outbreaks [28]. In vineyards, spiders and generalist predatory insects form diverse communities [29,30,31] and can contribute to the control of vineyard pests [32,33,34,35,36]. The richness of predators can be negatively influenced by cultural practices and pesticide applications while also being favoured by the presence of surrounding groves and permanent inter-row vegetation [37,38,39,40,41].
In several studies, no negative effects of kaolin were reported for spiders (Araneae), Heteroptera and Coleoptera Coccinellidae both in orchards and cotton [42,43,44,45,46]. However, kaolin reduced the abundance of these generalist predatory taxa in other studies conducted in orchards [5,6,47,48,49].
The effects of kaolin on non-target arthropods in vineyards are still poorly understood. Two consecutive kaolin applications did not affect the parasitisation of H. vitis and Z. rhamni eggs by Anagrus atomus (L.) [11], whereas kaolin was moderately harmful to the phytoseiid mites Typhlodromus pyri Scheuten and Kampimodromus aberrans (Oudemans) both in the field and in laboratory trials [50]. The adoption of bunch-zone leaf removal did not substantially affect phytoseiid populations in vineyards [50]. However, no literature data are available to determine if this cultural practice could negatively affect other generalist predators as a result of changes that occur in the structure and microclimate of the grapevine canopy [23]. Therefore, in some vineyards, the effects of kaolin and bunch-zone leaf removal on the diversity and amount of spiders and generalist predatory insects were studied.

2. Materials and Methods

2.1. Study Vineyards

The study was conducted in 2015 and 2016 in three vineyards located in a flat grape-growing area of north-eastern Italy (Gorizia district, Friuli Venezia Giulia region), in the framework of trials against H. vitis and Z. rhamni [11] and L. botrana [17], herein named Vineyard A (2015 and 2016), Vineyard B (2015) and Vineyard C (2016). Vineyard A (45°57′51″ N, 13°26′49″ E, 56 m a.s.l., cultivar Pinot Gris) was a 10-year-old conventional vineyard, with grapevines grown using the Guyot training system and distanced between and along rows of 2.5 m and 0.8 m, respectively. Vineyard B (45°57′20″ N, 13°26′50″ E, 50 m a.s.l., cultivar Pinot Gris) was a 30-year-old organic vineyard with grapevines grown using the double-arched Guyot training system and distanced between and along rows of 2.8 m and 1 m, respectively. Vineyard C (45°58′02″ N, 13°31′31″ E, 53 m a.s.l., cultivar Pinot Gris) was a 15-year-old organic vineyard with grapevines grown using the Guyot training system and distanced between and along rows of 2.2 m and 0.7 m, respectively. In the three vineyards, herbaceous vegetation on the inter-rows was present. During the two-year study, standard fungicide programs were followed and insecticides were not applied. In terms of fungicides, in Vineyards B and C, only copper and sulphur products were used, whereas in Vineyard A, synthetic substances were also sprayed.

2.2. Experimental Design

In all vineyards, the effects of kaolin and bunch-zone leaf removal (LR) were studied and, only in Vineyard A, they were evaluated for two consecutive years. Kaolin (Surround WP, Tessenderlo Kerley Inc., Phoenix, AZ, USA, 2% suspension) was sprayed at the rate of 1000 L/ha two times a year, except on Vineyard A in 2016 where three applications occurred because the first was notably washed off by rain [16] (Table 1). Kaolin was applied at the occurrence of defined L. botrana phenological stages as previously reported [17]. All applications were performed using a backpack sprayer (Oleo-Mac, Sp-126, Emak S.p.A., Bagnolo in Piano RE, Italy).
In all vineyards, a randomised block design with four replicates, each corresponding to a different grapevine row, was adopted. Blocks were divided into two plots (kaolin and control), each consisting of 28 (Vineyard A) or 20 (Vineyard B) or 24 (Vineyard C) grapevines. In half of the grapevines of each plot, leaves were manually removed so to obtain two subplots, with and without LR (LR and no LR) (Table 1). In Vineyard A, the plots sprayed with kaolin and subplots subjected to LR were the same in the two years.

2.3. Samplings

In 2015 and 2016, spider amount was assessed by a drop cloth method (in 2015 in both Vineyards A and B: 11, 22, 29 June, and 6 July; in 2016 in Vineyard A: 6, 20, 28 June, and 6 July; in 2016 in Vineyard C: 7, 21 June, and 1, 8 July). Only in 2015, both spiders and generalist predatory insects were monitored using yellow sticky traps that were replaced weekly (Vineyards A and B, from 4 June to 18 August). Yellow sticky traps were used in 2015 because they are an effective sampling method for leafhoppers which were considered only during this year [11]. For both sampling methods, the first sampling was carried out before the first kaolin application. The drop cloth method consisted of manually shaking a grapevine canopy five times, grabbing the apical part of the trunk, and collecting fallen spiders on a pale cloth sheet (65 × 45 cm). At each sampling date, the spiders collected on 10 grapevines in the central part of each subplot were separately preserved in vials with 70% aqueous ethanol. Yellow sticky traps (20 × 10 cm) were smeared with glue (Temo-O-Cid®, Kollant Srl, Vigonovo, VE, Italy) and hung on the horizontal wires of the grapevine trellis at about 1.5 m from the ground level to be inside the canopy, but not covered by leaves. At each sampling date, one trap per subplot was installed.
Spiders and generalist predatory insects were observed in the laboratory under a dissecting microscope. Spiders collected with the drop cloth method were identified to different taxonomic levels, i.e., adults were assigned to genus or species and juvenile individuals to family or genus. In addition, they were grouped on the basis of hunting strategy (i.e., web-builders and hunters, with the latter further divided into ambushers and active hunters), and body size (i.e., ≤4 mm, small; 4.1–7 mm, medium; 7.1–10 mm, large). The distance from the front of the carapace, without the chelicerae, to the end of the abdomen was measured. Among predatory insects captured by yellow sticky traps, the following taxa were identified: Aeolothrips sp. (Thysanoptera: Aeolothripidae), Scymninae (Coleoptera: Coccinellidae), and Coccinellidae non-Scymninae, Chrysoperla carnea s.l. (Stephens) (Neuroptera: Chrysopidae), and Orius sp. (Hemiptera: Anthocoridae). Among spiders captured by yellow sticky traps, web-builders were distinguished from hunters, which were separately counted at the family level.

2.4. Statistical Analyses

The effects of kaolin and LR on the spider communities collected with the drop cloth method in the three vineyards were examined in terms of species diversity (Shannon index H’), three functional diversity (FD) indices [i.e., functional richness (width of a niche space filled with species), functional evenness (the evenness of the distribution of species abundance in niche space) and functional distance (mean of individual species to the centroid of all species in the community)] and functional guilds (i.e., body size and hunter percentage) [52,53]. All indices were calculated using the FD package [53,54], which implements a distance-based approach that allows for the analysis of both continuous and categorical variables. The data relative to H’ and FD indices, and functional guilds for spiders (collected with drop cloth) were compared using an ANOVA test applied to linear mixed-effects models (LMM) [55]. For these analyses, spider community data of Vineyard A were pooled at the year level to highlight whether the effect of kaolin and LR recorded in each year was consistent. For the same comparisons, the data collected in the two Vineyards B and C were pooled to highlight whether the effects of kaolin and LR were consistent. The sampling date was included in the models as a random factor. Model assumptions were verified by visual inspection of diagnostic plots. When assumptions were violated, a logarithmic transformation was applied. Changes in spider species assemblage among all factors were inspected using a multivariate approach. A Kruskal’s non-metric multidimensional scaling (NMDS) unconstrained ordination [56,57] was performed with the Bray-Curtis (dis)similarity index, two dimensions (k = 2) on Wisconsin and square root transformed data, separately for Vineyard A (stress = 0.11) and Vineyards B and C (stress = 0.14). All the multivariate analyses were performed using the “vegan” R package [58].
To evaluate the effects of kaolin and LR on the number of spiders and predatory insects (collected with a drop cloth and yellow sticky traps), for each vineyard and year, an ANOVA test applied to linear mixed-effects models (LMM) followed by Tukey’s post hoc test was used [59]. The sampling date was included in the models as a random factor. Model assumptions were verified by visual inspection of diagnostic plots. When assumptions were violated, a logarithmic transformation was applied.
Within spiders, the relative proportion of hunting-strategy groups (hunters and web-builders) or subgroups (ambushers and active hunters) in each vineyard was compared using a G test of goodness of fit. To compare percentage data, a Fisher’s exact test or Ryan’s test [60] were used when two or more proportions were considered, respectively.
Statistical analyses were performed with SPSS version 20 [61] or R software version R 4.0.4 [62].

3. Results

3.1. Spiders and Generalist Predatory Insects in Vineyards

3.1.1. Spiders by the Drop Cloth Method

Spider populations were more than twice as abundant in Vineyard B (N. 160) compared to the other vineyards (A 2015: N. 70; A 2016: N. 65; C: N. 60). In whole, spiders belonged to nine families (the web-builders Araneidae, Linyphiidae and Theridiidae; the ambushers Thomisidae; and the active hunters Gnaphosidae, Miturgidae, Oxyopidae, Salticidae and Sparassidae) and 28 different taxa (Table S1 in the Supplementary Materials). The highest diversity in the number of families was observed in 2016 in Vineyard A (nine out of nine), but no less than seven families were observed in the other cases (i.e., Vineyard A and B in 2015 and Vineyard C in 2016).
Based on the hunting strategy, hunters were more represented than web-builders with significant differences at the G test in Vineyard A (in 2015: 76%, p < 0.0001; in 2016: 72%, p < 0.0001) and in Vineyard B (62%, p < 0.001), but not in Vineyard C (58%, p = 0.13). The proportion of web-builders was significantly higher in Vineyards B and C than in Vineyard A at 0.05 level (Ryan’s test).
Among web-builders, Araneidae were prevalent in all vineyards (Vineyard A in 2015: 71%, p = 0.056; Vineyard A in 2016: 61%, p = 0.28; Vineyard B: 52%, p = 0.97; Vineyard C: 68%, p = 0.044), with a prevalence of Nuctenea sp. in Vineyard A and Vineyard C, and Mangora acalypha (Walckenaer) in Vineyard B. In total, Linyphiidae represented around a third of web-builders.
Among hunters, the subgroup “ambushers”, exclusively represented by Thomisidae, was on average prevalent on the subgroup “active hunters” in Vineyard A and Vineyard B, even if the difference did not reach the significance level at the G test (Vineyard A in 2015: 58%, p = 0.15; Vineyard A in 2016: 57%, p = 0.23; Vineyard B: 54%, p = 0.45), whereas the subgroup “active hunters” was significantly prevalent in Vineyard C (80%, p < 0.0001). Among ambushers (i.e., Thomisidae), Xysticus sp. (60%) was the prevalent taxon. Among active hunters, Oxyopidae of the genus Oxyopes (40%) and Salticidae (36%) were the more represented.

3.1.2. Predatory Arthropods by Yellow Sticky Traps

In both Vineyards A and B, the amount of captured predatory insects belonging to the considered taxa was prevalent on spiders (84% and 16% of capture, respectively) (Table S2 in the Supplementary Materials). Among the predatory insects, Aeolothrips sp. was the most abundant (85% in Vineyard A, and 71% in Vineyard B). The number of captured Coccinellidae in Vineyard B was three times higher than in Vineyard A.
Total spiders were more abundant in Vineyard B than in Vineyard A, but the proportion of web-builders and hunters was the same (40% and 60%, respectively) (Table S2 in the Supplementary Materials). Among hunters, Thomisidae were the most abundant family in both vineyards (around 51%).

3.2. Effect of Kaolin and Bunch-Zone Leaf Removal on Predatory Insects and Spiders

3.2.1. Vineyard A

During the two years under study (2015 and 2016), spiders collected by the drop cloth method were not affected by kaolin and LR in terms of H’ and FD indices and functional guilds (i.e., body size and hunter percentage) (Table 2). The interactions among factors were not significant, suggesting a lack of a cumulative effect on the spider community. However, a sensitive shift in the spider community was observed for year, kaolin and LR (Figure 1a). NMDS1 discriminated mainly between 2015 and 2016 and partially between LR and no LR subplots, while NMDS2 discriminated mainly between kaolin and the control. Kaolin (NMDS2) was associated with a higher abundance of Xysticus sp., while Oxyopes sp. was more frequent in the control.
Significant differences in spider amount occurred only at the family level, i.e., for active hunters Oxyopidae in 2015 and Salticidae in 2016, and for web-builders Araneidae in 2016 (Table 3). No significant differences were observed for LR compared to no LR.
Among predatory insects captured by yellow sticky traps in 2015, kaolin significantly increased Scymninae (Table 4). On the contrary, Orius sp. showed lower captures in the kaolin than in the control, but not at a significant level. Aeolothrips sp. showed significantly higher captures in LR than no LR. Spiders captured by yellow sticky traps were not significantly affected by either kaolin or LR. Concerning spider families, Thomisidae showed higher captures in LR than no LR, but not at a significant level.

3.2.2. Vineyards B and C

In neither of the two vineyards were spiders collected by the drop cloth method affected by kaolin in terms of H’ and FD indices and considered functional guilds (i.e., body size and hunter percentage) (Table 5). On other hand, LR significantly decreased H’ and functional evenness (Table 5), mostly in Vineyard C when combined with kaolin (Figure 2). The comparison of the two vineyards showed significantly higher H’, functional richness and evenness in Vineyard B compared to Vineyard C (Table 5 and Figure 2). NMDS analysis showed that the two vineyards had different spider communities (NMDS1, Figure 1b). Kaolin did not influence the spider community, while LR produced a significant change in the spider community shown along the NMDS2. In particular, LR favoured the abundance of Xysticus sp., while no LR resulted in a higher occurrence of Oxyopes lineatus Latreille.
The total spiders collected by the drop cloth method in both vineyards were not significantly affected by kaolin and LR, not even when considering hunting-strategy groups or families (Table 6). The proportion of the active hunters on the total hunters [i.e., ambushers (Thomisidae) plus active hunters] was not changed by kaolin in both Vineyards B and C (Vineyard B: from 57% to 40%, p = 0.23; Vineyard C: constant 86%, p = 1.0).
Among the predatory insects captured by yellow sticky traps in vineyard B, lower captures of Orius sp. in the kaolin than in the control were recorded (Table 7). Predatory insects were not influenced by LR. Spiders were not significantly affected by either kaolin or LR.

3.2.3. Comparison between the Two Sampling Methods

In 2015, in Vineyard A, a significantly higher percentage of web-builders than hunters was associated with yellow sticky traps compared to the drop cloth method (42% vs. 24%, p = 0.007, at Fisher’s exact test). This occurrence was not confirmed for Vineyard B (38% vs. 40%, p = 0.766, at Fisher’s exact test). Among hunters, a significantly higher percentage of Salticidae was captured with yellow sticky traps than by the drop cloth method (Vineyard A: 34% vs. 9%, p = 0.0007, at Fisher’s exact test; Vineyard B: 23% vs. 11%, p = 0.017).

4. Discussion

4.1. Spiders and Generalist Predatory Insects in Vineyards

The same taxa of spiders found in the vineyards of the present study are reported as predators of L. botrana larvae, pupae and adults in other studies [34,63,64,65]. For example, Salticus scenicus (Clerck) (Salticidae), recorded in the present study, has been reported feeding on H. vitis nymphs in French vineyards, although its contribution to leafhopper control has not been considered important [66]. In Portuguese vineyards, as well as in the present study, H. vitis dead adults were found on spider webs [65]. Oxyopes lineatus (Oxyopidae), whose individuals were observed preying on H. vitis adults during the present study, has been reported feeding on Cicadellidae [67]. Even Linyphiidae, found in low numbers in the present study, could have a role in the control of H. vitis, as the species Bathyphantes pallidus (Banks) was found to be a valuable predator of the leafhopper Empoasca fabae (Harris) in a field of alfalfa in Kentucky (USA) [68]. Moreover, in American vineyards, Salticidae and Theridiidae have been reported as effective predators of Erythroneura spp. leafhoppers [69], even if plant vigour or other factors that favour Anagrus spp. egg parasitoids, seem to be more important than spider abundance [32,33,70]. Finally, species of Cheiracanthium sp. (Miturgidae), also found in two vineyards in the present study, are widespread predators of Erythroneura spp. leafhoppers in Californian vineyards [35,36,38,71].
Among web-builders, the prevalence of Araneidae in the present study is in agreement with other studies [30,72]. Their higher abundance in both Vineyards B and C compared to Vineyard A could be associated with the synthetic insecticides applied in the previous years in this last vineyard [73,74]. To this purpose, under laboratory conditions, it was observed that the web of Araniella sp. (Araneidae) did not protect its owner from insecticide spraying [75]. Nevertheless, in an apple orchard, web builders (Theridiidae) resulted in being less susceptible to insecticide spraying than hunters probably because their three-dimensional webs protected them from droplets [76].
The comparison of yellow sticky traps and drop cloth to monitor spiders in vineyards was performed in the present study and in that of Nobre et al. [77]. Both studies are in agreement with the higher amount of web-builders captured by yellow sticky traps than the drop cloth method. Additionally, among hunters, a relatively higher proportion of Salticidae captured by yellow sticky traps compared with the drop cloth method was observed in both studies. When the canopy is shaken, the Salticidae individuals could jump outside the surface area of the pale cloth sheet resulting in an underestimation of their number. Moreover, according to Nobre et al. [77], the moving of Salticidae along leaves and wires could increase their interception by traps. In agreement with Nobre et al. [77], we can state that the yellow sticky traps are not sufficiently representative of the spider fauna in vineyards since they alter the effective proportion among spider families. Furthermore, the drop cloth method is more suitable for species identification.
The five taxa of generalist predatory insects captured by yellow sticky traps (i.e., Aeolothrips sp., Scymninae, Coccinellidae non-Scymninae, Orius sp. and C. carnea s.l.) are reported feeding on grapevine pests. Aeolothrips sp. are predators of phytophagous thrips in vineyards [78]. Scymninae presence in vineyards is often associated with mealybug infestation [79]. Chrysoperla carnea s.l. is reported as a predator of L. botrana larvae [63,65] and motile forms of H. vitis and Z. rhamni [80]. The generalist pirate bugs Orius spp. are effective control agents of tetranychid and eriophyid mites in vineyards [29], but can also feed on H. vitis [81]. In that regard, a strong correlation between H. vitis and Orius niger (Wolff) population densities was observed using yellow sticky traps, even if the predatory activity could not be confirmed visually [82]. In Californian vineyards, low densities of leafhoppers and thrips were attributed to the impacts of Orius spp. and coccinellids (see Miles et al. [39]).

4.2. Influence of Kaolin and Bunch-Zone Leaf Removal on Spiders and Generalist Predatory Insects

In this study, kaolin affected the spider communities in terms of abundance only in three cases recorded in Vineyard A, i.e., the Oxyopidae and Salticidae active hunters, and the Araneidae web-builders. The prevalence of cases with negative kaolin effects on hunters compared to web-builders agrees with studies conducted in apple orchards [44,47]. Concerning the web builders, a higher mortality of Araniella cucurbitina (Clerck) was observed under laboratory conditions after the ingestion of great amounts of silk covered with kaolin [83], it is because Araneidae often repair or rebuild their webs by ingesting them [25]. This feeding behaviour can explain why in our study Araneidae appeared to be more sensitive to kaolin than the other web-builder spiders.
In the present study, the relatively reduced negative effects of kaolin on spiders can be explained by the low number (two or three) of kaolin applications (20 kg/ha per application). In the literature, negative effects on spiders were sometimes observed with a higher number of kaolin applications than in the present study (total amount per hectare 5–10 times higher) [6,42,44,46,47]. In apple orchards, after 12 kaolin applications (45 kg/ha per application), spider densities were significantly reduced [47], and at more than four weeks from the last application the abundance of spiders was still significantly lower in the kaolin-treated plots [6]. On the other hand, in a cotton field, spider densities were not reduced after several weekly kaolin applications (24–50 kg/ha per application) [46]. In an apple orchard, a negative effect of kaolin on spiders was observed only in the second year after four yearly applications (60 kg/ha per application) [44]. Even in a pecan orchard, after seven and six kaolin applications (50 kg/ha per application) in the first and second year, respectively, spiders became fewer on kaolin-treated plots in the second year [42]. In Vineyard A of the present study, a reduction in the abundance of Araneidae and Salticidae was observed only in the second of two consecutive years of application of kaolin on the same plots, even though the species diversity of spiders increased in comparison to the first year. After all, the heavy reduction of H. vitis and Z. rhamni populations in plots sprayed with kaolin [11,17] could have reduced the availability of prey for hunters causing their dispersion. The absence of negative effects on Thomisidae, and even an average increase in their populations observed in some cases, could be explained by the reduction of intra-guild predation by the active hunters when they disperse [27,84,85,86].
Two kaolin applications interfered with the abundance of predatory insects only in two cases: Orius sp. decreased and Scymininae increased. With the same number of kaolin applications, a negative effect on Orius sp. was also reported in olive orchards [5]. For another minute pirate bug, Anthocoris nemoralis (Fabricius) (Anthocoridae), negative effects of kaolin were found under laboratory and field conditions [5,87], but this occurrence was not confirmed by another laboratory study [88]. In the present study, the lower population of Orius sp. could also be an indirect effect of the reduction of leafhopper populations by kaolin [11], as anthocorids can have a role in H. vitis control [81,82]. In Vineyard A, the higher densities of Scymninae observed in the kaolin compared to the control plots could be explained because kaolin can favour mealybug abundance [89,90].
In the present study, kaolin did not affect Coccinellidae non-Scymninae in agreement with other studies [42,43,46], even if negative effects have been reported in some cases [5,44]. However, in the laboratory, kaolin was harmless to these Coccinellidae [87,91].
Additionally, in the present study, C. carnea s.l. was not negatively influenced by kaolin, although the data reported in the literature did not always confirm the absence of negative effects [45,92]. However, in the laboratory kaolin was harmless to C. carnea and Chrysoperla externa (Hagen) [87,88,93]. Kaolin did not negatively affect Aeolothrips sp., whose individuals spend most of their life feeding on small arthropods and pollen occurring in herbaceous vegetation of the inter-row.
Bunch-zone leaf removal influenced captures of spiders and predatory insects only in two cases: Aeolothrips sp. that were more abundant in LR of Vineyard A and spiders that showed lower species diversity and functional evenness in Vineyard C. The increase in captures of Aeolothrips can be explained by the preference of Thysanoptera for yellow sticky traps exposed to sunlight [94,95] as occurred for traps placed on grapevines submitted to LR.
Regarding the effect of LR on the spider community, which significantly reduced spider diversity in one of the three vineyards, opposing suggestions were reported in the literature. The study of Pennington et al. [96], in which grapevines grown with minimal or intensive pruning were compared, did not show the negative effects of a more reduced canopy. On the contrary, a higher number of hunters and web-builders was attributed to the abundant foliage on apple trees [97].

5. Conclusions

In vineyards, moderate use of kaolin and the application of LR have shown minor impact on spiders and generalist predatory insects; therefore, they are suitable cultural practices in the context of IPM strategies. The negative effects are also negligible after two consecutive years of kaolin applications on the same plots. Even the few cases of a decrease in hunter spiders could be a consequence of the negative effects of kaolin on leafhoppers, which are the most frequent prey of spiders inhabiting grapevine canopy. Regardless, considering the positive effects of kaolin and LR on the control of grapevine key pests, the overall outcome of their adoption is positive. The use of these cultural practices in the context of IPM reduces the risk that pests exceed their economic thresholds and, thus, the need for insecticide applications in vineyard.

Supplementary Materials

The following supporting information can be downloaded at: https://www.mdpi.com/article/10.3390/insects14020126/s1, Table S1: Spiders collected with the drop cloth method; Table S2: Arthropods captured by yellow sticky traps.

Author Contributions

E.C., F.P., F.T. and P.Z. conceived and designed the research. E.C., F.P., F.T. and P.Z. conducted field trials. E.C. identified the arthropods. F.B., F.P. and F.T. analysed the data. All authors have read and agreed to the published version of the manuscript.

Funding

This research received no external funding.

Data Availability Statement

Data available upon request.

Acknowledgments

The authors would like to thank the vineyard owners who kindly offered their properties as trial sites: Federico Bigot, Renzo Sgubin, and Denis and Patrick Sturm. The authors also thank Elisabetta Tilatti for her collaboration in the field trials.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Glenn, D.M.; Puterka, G.; Vanderzwet, T.; Byers, R.E.; Feldhake, C. Hydrophobic particle films: A new paradigm for suppression of arthropod pests and plant diseases. J. Econ. Entomol. 1999, 92, 759–771. [Google Scholar] [CrossRef] [Green Version]
  2. Salerno, G.; Rebora, M.; Kovalev, A.; Gorb, E.; Gorb, S. Kaolin nano-powder effect on insect attachment ability. J. Pest Sci. 2020, 93, 315–327. [Google Scholar] [CrossRef]
  3. Vincent, C.; Hallman, G.; Panneton, B.; Fleurat-Lessard, F. Management of agricultural insects with physical control method. Annu. Rev. Entomol. 2003, 48, 261–281. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  4. Unruh, T.R.; Knight, A.L.; Upton, J.; Glenn, D.M.; Puterka, G.J. Particle films for suppression of the codling moth (Lepidoptera: Tortricidae) in apple and pear orchards. J. Econ. Entomol. 2000, 93, 737–743. [Google Scholar] [CrossRef] [PubMed]
  5. Pascual, S.; Cobos, G.; Seris, E.; González-Núñez, M. Effects of processed kaolin on pests and non-target arthropods in a Spanish olive grove. J. Pest Sci. 2010, 83, 121–133. [Google Scholar] [CrossRef]
  6. Markό, V.; Blommers, L.H.M.; Bogya, S.; Helsen, H. Kaolin particle films suppress many apple pests, disrupt natural enemies and promote woolly apple aphid. J. Appl. Entomol. 2008, 132, 26–35. [Google Scholar] [CrossRef]
  7. Lo Verde, G.; Caleca, V.; Lo Verde, V. The use of kaolin to control Ceratitis capitata in organic citrus groves. Bull. Insectol. 2011, 64, 229–273. [Google Scholar]
  8. Marcotegui, A.; Sánchez-Ramos, I.; Pascual, S.; Fernández, C.E.; Cobos, G.; Armendáriz, I.; Cobo, A.; González-Núñez, M. Kaolin and potassium soap with thyme essential oil to control Monosteira unicostata and other phytophagous arthropods of almond trees in organic orchards. J. Pest Sci. 2015, 88, 753–765. [Google Scholar] [CrossRef]
  9. Xu, Y.; Dietrich, C.H.; Zhang, Y.-L.; Dmitriev, D.A.; Zhang, L.; Wang, Y.-M.; Lu, S.-H.; Qin, D.-Z. Phylogeny of the tribe Empoascini (Hemiptera: Cicadellidae: Typhlocybinae) based on morphological characteristics, with reclassification of the Empoasca generic group. Syst. Entomol. 2021, 46, 266–286. [Google Scholar] [CrossRef]
  10. Abedini, R.; Frarazmand, H.; Jebeleh, E.; Sirjani, M. Effect of kaolin clay (WP 95%) on grape leafhopper, Arboridia kermanshah Dlabola (Hem: Cicadellidae) in field condition. Plant Pest Res. 2017, 7, 1–8. [Google Scholar] [CrossRef]
  11. Tacoli, F.; Pavan, F.; Cargnus, E.; Tilatti, E.; Pozzebon, A.; Zandigiacomo, P. Efficacy and mode of action of kaolin in the control of Empoasca vitis and Zygina rhamni (Hemiptera: Cicadellidae) in vineyards. J. Econ. Entomol. 2017, 110, 1164–1178. [Google Scholar] [CrossRef] [PubMed]
  12. Tacoli, F.; Mori, N.; Pozzebon, A.; Cargnus, E.; Da Vià, S.; Zandigiacomo, P.; Duso, C.; Pavan, F. Control of Scaphoideus titanus with natural products in organic vineyards. Insects 2017, 8, 129. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  13. Tirello, P.; Marchesini, E.; Gherardo, P.; Raniero, D.; Rossetto, F.; Pozzebon, A.; Duso, C. The control of the American leafhopper Erasmoneura vulnerata (Fitch) in European vineyards: Impact of synthetic and natural insecticides. Insects 2021, 12, 85. [Google Scholar] [CrossRef] [PubMed]
  14. Sleezer, S.; Johnson, D.T.; Lewis, B.; Goggin, F.; Rothrock, C.; Savin, M. Foliar grape phylloxera, Daktulosphaira vitifoliae (Fitch), seasonal biology, predictive model and management in the Ozarks region of the United States. Acta Hortic. 2011, 904, 151–156. [Google Scholar] [CrossRef]
  15. Valizadeh, H.; Abbasipour, H.; Farazmand, H.; Askarianzadeh, A. Evaluation of kaolin application on oviposition control of the vine cicada, Psalmocharias alhageos in vineyards (Homoptera: Cicadidae). Entomol. Gen. 2013, 34, 279–286. [Google Scholar] [CrossRef]
  16. Pease, C.E.; Lόpez-Olguín, J.F.; Pérez-Moreno, I.; Marco-Mancebόn, V. Effects of kaolin on Lobesia botrana (Lepidoptera: Tortricidae) and its compatibility with the natural enemy, Trichogramma cacoeciae (Hymenoptera: Trichogrammatidae). J. Econ. Entomol. 2016, 109, 740–745. [Google Scholar] [CrossRef]
  17. Tacoli, F.; Cargnus, E.; Kiaeian Moosavi, F.; Zandigiacomo, P.; Pavan, F. Efficacy and mode of action of kaolin and its interaction with bunch-zone leaf removal against Lobesia botrana on grapevines. J. Pest Sci. 2019, 92, 465–475. [Google Scholar] [CrossRef]
  18. Linder, C.; Staehli, N.; Leumann, M.; Siegfried, W.; Kehrli, P. Physical barriers against Drosophila suzukii in viticulture. IOBC/WPRS Bull. 2018, 139, 35–39. [Google Scholar]
  19. Isaacs, R.; Mercader, R.J.; Wise, J.C. Activity of conventional and reduced-risk insecticides for protection of grapevines against the rose chafer, Macrodactylus subspinosus (Coleoptera: Scarabaeidae). J. Appl. Entomol. 2004, 128, 371–376. [Google Scholar] [CrossRef]
  20. Maier, R.M.; Williamson, R.C. Evaluation of kaolin clay as an alternative management tactic for Japanese beetle feeding damage in grape vineyards. J. Hortic. 2016, 3, 184. [Google Scholar] [CrossRef] [Green Version]
  21. Percival, D.C.; Fisher, K.H.; Sullivan, J.A. Use of fruit zone leaf removal with Vitis vinifera L. cv Riesling grapevines. II. Effects on fruit composition, yield, and occurrence of bunch rot (Botrytis cinerea Pers.). Am. J. Enol. Vitic. 1994, 45, 133–139. [Google Scholar] [CrossRef]
  22. Pavan, F.; Cargnus, E.; Kiaeianmoosavi, F.; Bigot, G.; Tacoli, F.; Zandigiacomo, P. Bunch-zone leaf removal of grapevines to prevent damage by Lobesia botrana and grey mould. Bull. Insectol. 2016, 69, 107–115. [Google Scholar]
  23. Kiaeian Moosavi, F.; Cargnus, E.; Pavan, F.; Zandigiacomo, P. Effects of grapevine bunch exposure to sunlight on berry surface temperature and Lobesia botrana (Lepidoptera: Tortricidae) egg laying, hatching and larval settlement. Agric. For. Entomol. 2018, 20, 420–432. [Google Scholar] [CrossRef] [Green Version]
  24. Hosseinabad, A.; Khadivi, A. Foliar application of kaolin reduces the incidence of sunburn in ‘Thompson seedless’ grapevine. Eur. J. Hortic. Sci. 2019, 84, 171–176. [Google Scholar] [CrossRef] [Green Version]
  25. Marc, P.; Canard, A.; Ysnel, F. Spiders (Araneae) useful for pest limitation and bioindication. Agric. Ecosyst. Environ. 1999, 74, 229–273. [Google Scholar] [CrossRef]
  26. Symondson, W.O.C.; Sunderland, K.D.; Greenstone, M.H. Can generalist predators be effective biocontrol agents? Annu. Rev. Entomol. 2002, 47, 561–594. [Google Scholar] [CrossRef] [Green Version]
  27. Nyffeler, M.; Sunderland, K.D. Composition, abundance and pest control potential of spider communities in agroecosystems: A comparison of European and US studies. Agric. Ecosyst. Environ. 2003, 95, 579–612. [Google Scholar] [CrossRef]
  28. Harwood, J.D.; Obrycki, J.J. The role of alternative prey sustaining predator populations. In Proceedings of the Second International Symposium on Biological Control of Arthropods, Davos, Switzerland, 12–16 September 2005; pp. 453–462. [Google Scholar]
  29. Duso, C.; Girolami, V. Ruolo degli Antocoridi nel controllo del Panonychus ulmi Koch nei vigneti. Boll. Ist. entomol. Univ. studi Bologna 1982, 37, 157–169. [Google Scholar]
  30. Isaia, M.; Bona, F.; Badino, G. Influence of landscape diversity and agricultural practices on spider assemblage in Italian vineyards of Langa Astigiana (Northwest Italy). Environ. Entomol. 2006, 35, 297–307. [Google Scholar] [CrossRef] [Green Version]
  31. Thiéry, D.; Louâpre, P.; Muneret, L.; Rusch, A.; Sentenac, G.; Vogelweith, F.; Moreau, J. Biological protection against grape berry moths. A review. Agron. Sustain. Dev. 2018, 38, 15. [Google Scholar] [CrossRef] [Green Version]
  32. Costello, M.J.; Daane, K.M. Spider and leafhopper (Erythroneura spp.) response to vineyard ground cover. Environ. Entomol. 2003, 32, 1085–1098. [Google Scholar] [CrossRef] [Green Version]
  33. Wilson, H.; Miles, A.F.; Daane, K.M.; Altieri, M.A. Vineyard proximity to riparian habitat influences Western grape leafhopper (Erythroneura elegantula Osborn) populations. Agric. Ecosyst. Environ. 2015, 211, 43–50. [Google Scholar] [CrossRef]
  34. Nobre, T.; Meierrose, C. The species composition, within-plant distribution, and possible predatory role of spiders (Araneae) in a vineyard in southern Portugal. In Proceedings of the 18th European Colloquium of Arachnology, High Tatras, Slovakia, 12–17 July 1999; Gajdoš, P., Pekar, S., Eds.; Ekológia (Bratislava), 19, suppl. 3/2000. pp. 193–200. [Google Scholar]
  35. Hogg, B.N.; Daane, K.M. Ecosystem services in the face of invasion: The persistence of native and non-native spiders in an agricultural landscape. Ecol. Appl. 2011, 21, 565–576. [Google Scholar] [CrossRef] [PubMed]
  36. Hogg, B.N.; Daane, K.M. The roles of top and intermediate predators in herbivore suppression: Contrasting results from the field and laboratory. Ecol. Entomol. 2014, 39, 149–158. [Google Scholar] [CrossRef]
  37. Altieri, M.A.; Ponti, L.; Nicholls, C.I. Manipulating vineyard biodiversity for improved insect pest management: Case studies from northern California. Int. J. Biodivers. Sci. Manag. 2005, 1, 191–203. [Google Scholar] [CrossRef]
  38. Hogg, B.N.; Daane, K.M. The role of dispersal from natural habitat in determining spider abundance and diversity in California vineyards. Agric. Ecosyst. Environ. 2010, 135, 260–267. [Google Scholar] [CrossRef]
  39. Miles, A.; Wilson, H.; Altieri, M.; Nicholls, C. Habitat diversity at the field and landscape level: Conservation biological control research in California viticulture. In Arthropod Management in Vineyards: Pest, Approaches, and Future Directions; Bostanian, N.J., Vincent, C., Isaac, R., Eds.; Springer Science + Business Media B.V.: Dordrecht, The Netherlands, 2012; pp. 159–189. [Google Scholar] [CrossRef]
  40. Judt, C.; Guzmán, G.; Gómez, J.A.; Cabezas, J.M.; Entrenas, J.A.; Winter, S.; Zaller, J.G.; Paredes, D. Diverging effects of landscape factors and inter-row management on the abundance of beneficial and herbivorous arthropods in Andalusian vineyards (Spain). Insects 2019, 10, 320. [Google Scholar] [CrossRef] [Green Version]
  41. Zanettin, G.; Bullo, A.; Pozzebon, A.; Burgio, G.; Duso, C. Influence of vineyard inter-row groundcover vegetation management on arthropod assemblages in the vineyards of north-eastern Italy. Insects 2021, 12, 349. [Google Scholar] [CrossRef]
  42. Lombardini, L.; Harris, M.K.; Glenn, D.M. Effects of particle film application on leaf gas exchange, water relations, nut yield, and insect populations in mature pecan trees. HortScience 2005, 40, 1376–1380. [Google Scholar] [CrossRef] [Green Version]
  43. Karagounis, C.; Kourdoumbalos, A.K.; Margaritopoulos, J.T.; Nanos, G.D.; Tsitsipis, J.A. Organic farming-compatible insecticides against the aphid Myzus persicae (Sulzer) in peach orchards. J. Appl. Entomol. 2006, 130, 150–154. [Google Scholar] [CrossRef]
  44. Sackett, T.E.; Buddle, C.M.; Vincent, C. Effects of kaolin on the composition of generalist predator assemblages and parasitism of Choristoneura rosaceana (Lep.; Tortricidae) in apple orchards. J. Appl. Entomol. 2007, 131, 478–485. [Google Scholar] [CrossRef]
  45. Porcel, M.; Cotes, B.; Campos, M. Biological and behavioral effects of kaolin particle film on larvae and adults of Chrysoperla carnea (Neuroptera: Chrysopidae). Biol. Control. 2011, 59, 98–105. [Google Scholar] [CrossRef]
  46. Santos, R.L.; dos Santos Neves, R.C.; Colares, F.; Torres, J.B. Parasitoids of boll weevil Anthonomus grandis and resident predators in kaolin-treated cotton. Semin.-Ciênc. Agrár. 2013, 34, 3463–3474. [Google Scholar] [CrossRef]
  47. Markό, V.; Bogya, S.; Kondorosy, E.; Blommers, L.H.M. Side effects of kaolin particle films on apple orchard bug, beetle and spider communities. Int. J. Pest Manag. 2010, 56, 189–199. [Google Scholar] [CrossRef]
  48. González-Núñez, M.; Pascual, S.; Cobo, A.; Seris, E.; Cobos, G.; Fernández, C.E.; Sánchez-Ramos, I. Copper and kaolin sprays as tools for controlling the olive fruit fly. Entomol. Gen. 2021, 41, 97–110. [Google Scholar] [CrossRef]
  49. Moraefi, M.; Seddigh, S.; Hamrahi, A. Influence of concentration and time of kaolin application on agronomic traits, canola aphid (Brevicoryne brassicae L.) and its natural enemies. J. Agroecol. 2021, 12, 723–740. [Google Scholar] [CrossRef]
  50. Tacoli, F.; Cargnus, E.; Pozzebon, A.; Duso, C.; Tirello, P.; Pavan, F. Side effects of kaolin and bunch-zone leaf removal on predatory mite population (Acari: Phytoseiidae) occurring in vineyards. J. Econ. Entomol. 2019, 112, 1292–1298. [Google Scholar] [CrossRef] [PubMed]
  51. Lorenz, D.H.; Eichhorn, K.W.; Bleiholder, H.; Klose, R.; Meier, U.; Weber, E. Growth stages of the grapevine: Phenological growth stages of the grapevine (Vitis vinifera L. ssp. vinifera). Codes and descriptions according to the extended BBCH scale. Aust. J. Grape Wine Res. 1995, 1, 100–103. [Google Scholar] [CrossRef]
  52. Villéger, S.; Mason, N.W.H.; Mouillot, D. New multidimensional functional diversity indices for a multifaceted framework in functional ecology. Ecology 2008, 89, 2290–2301. [Google Scholar] [CrossRef] [Green Version]
  53. Laliberté, E.; Legendre, P. A distance-based framework for measuring functional diversity from multiple traits. Ecology 2010, 91, 299–305. [Google Scholar] [CrossRef]
  54. Laliberté, E.; Legendre, P.; Shipley, B. FD: Measuring Functional Diversity from Multiple Traits, and Other Tools for Functional Ecology; R Package, Version 1.0-12; 2014. [Google Scholar]
  55. Pinheiro, J.; Bates, D.; DebRoy, S.; Sarkar, D.; Heisterkamp, S.; Van Willigen, B.; Ranke, J.; R Core Team. Nlme: Linear and Nonlinear Mixed Effects Models, R Package, Version: 3-1; 2017. Available online: https://cran.r-project.org/package=nlme (accessed on 1 October 2021).
  56. Legendre, P.; Legendre, L. Numerical Ecology, 2nd ed.; Elsevier: Amsterdam, The Netherlands, 1998. [Google Scholar]
  57. Wildi, O. Data Analysis in Vegetation Ecology, 2nd ed.; Wiley-Blackwell: Chichester, UK, 2013; p. 330. [Google Scholar]
  58. Oksanen, J.; Blanchet, F.G.; Friendly, M.; Kindt, R.; Legendre, P.; McGlinn, D.; Minchin, P.R.; O’Hara, R.B.; Simpson, G.L.; Solymos, P.; et al. Community Ecology Package; 2019; pp. 1–296. [Google Scholar]
  59. Zuur, A.F.; Ieno, E.N.; Walker, N.J.; Saveliev, A.A.; Smith, G.M. Mixed Effects Models and Extensions in Ecology with R; Springer: New York, NY, USA, 2009; ISBN 0387874577. [Google Scholar]
  60. Ryan, T.A. Significance tests for multiple comparisons of proportions, variances, and other statistics. Psychol. Bull. 1960, 57, 318–328. [Google Scholar] [CrossRef] [PubMed]
  61. IBM Corp. IBM SPSS Statistics for Windows, Version 20.0; IBM Corp: Armonk, NY, USA, 2011. [Google Scholar]
  62. R Core Team. R: A Language and Environment for Statistical Computing; R Foundation for Statistical Computing: Vienna, Austria, 2021; Available online: https://www.r-project.org/index.html (accessed on 1 October 2021).
  63. Marchesini, E.; Montà, L.D. Observations on natural enemies of Lobesia botrana (Den. & Schiff.) (Lepidoptera Tortricidae) in Venetian vineyards. Boll. Di Zool. Agrar. E Di Bachic. 1994, 26, 201–230. [Google Scholar]
  64. Addante, R.; Di Gioia, S.; Calculli, C.; Pollice, A. The impact of spiders (Araneae) on Lobesia botrana (Denis & Schiffermüller) population density. IOBC/WPRS Bull. 2008, 36, 221–231. [Google Scholar]
  65. Gonçalves, F.; Carlos, C.; Crespi, A.; Villemant, C.; Trivellone, V.; Goula, M.; Canovai, R.; Zina, V.; Crespo, L.; Pinheiro, L.; et al. The functional agrobiodiversity in the Douro demarcated region viticulture: Utopia or reality? Arthropods as a case-study—A review. Ciênc. Téc. Vitivinícola 2019, 34, 102–114. [Google Scholar] [CrossRef]
  66. Sentenac, G. Les antagonistes naturels d’Empoasca vitis Göth en Bourgogne. In Etude de Faisabilité D’une Lutte Biologique par Augmentation; Mondiaviti: Bordeaux, France, 1 et 2 Décembre 2004; pp. 25–37. [Google Scholar]
  67. Huseynov, E.F. Natural prey of the lynx spider Oxyopes lineatus (Araneae: Oxyopidae). Entomol. Fenn. 2007, 18, 144–148. [Google Scholar] [CrossRef]
  68. Harwood, J.D.; Obrycki, J.J. Web-site selection strategies of linyphiid spiders in alfalfa: Implications for biological control. Biocontrol 2007, 52, 451–467. [Google Scholar] [CrossRef]
  69. Costello, M.J.; Daane, K.M. Spider (Araneae) species composition and seasonal abundance in San Joaquin Valley grape vineyards. Environ. Entomol. 1995, 24, 823–831. [Google Scholar] [CrossRef] [Green Version]
  70. Hanna, R.; Zalom, F.G.; Roltsch, W.J. Relative impact of spider predation and cover crop on population dynamics of Erythroneura variabilis in a raisin grape vineyard. Entomol. Exp. Appl. 2003, 107, 177–191. [Google Scholar] [CrossRef]
  71. Hogg, B.N.; Daane, K.M. Diversity and invasion within a predator community: Impacts on herbivore suppression. J. Appl. Ecol. 2011, 48, 453–461. [Google Scholar] [CrossRef]
  72. Addante, R.; Pesarini, C.; Ranieri, G. Faunistic and ecological aspects of spiders (Araneae) on vineyards. IOBC/WPRS Bull. 2006, 29, 221–234. [Google Scholar]
  73. Wisniewska, J.; Prokopy, R.J. Pesticide effect on faunal composition, abundance, and body length of spiders (Araneae) in apple orchards. Environ. Entomol. 1997, 26, 763–766. [Google Scholar] [CrossRef]
  74. Mazzia, C.; Capowiez, Y.; Marliac, G.; Josselin, D.; Pasquet, A. Spinosad application in an apple orchard affects both the abundance of the spider Araneus diadematus and its web construction behaviour. Ecotoxicology 2020, 29, 389–397. [Google Scholar] [CrossRef] [PubMed]
  75. Pekár, S. Foraging mode: A factor affecting the susceptibility of spiders (Araneae) to insecticide applications. Pestic. Sci. 1999, 55, 1077–1082. [Google Scholar] [CrossRef]
  76. Pekár, S. Effect of IPM practices and conventional spraying on spider population dynamics in an apple orchard. Agric. Ecosyst. Environ. 1999, 73, 155–166. [Google Scholar] [CrossRef]
  77. Nobre, T.; Meierrose, C.; De Oliveira, N.G. Comparison of sampling techniques for vineyard foliage spiders (Araneae). In Proceedings of the 18th European Colloquium of Arachnology, High Tatras, Slovakia, 12–17 July 1999; Gajdoš, P., Pekar, S., Eds.; Ekológia (Bratislava), 19, suppl. 3/2000. pp. 201–206. [Google Scholar]
  78. Trdan, S.; Andjus, L.; Raspudić, E.; Kač, M. Distribution of Aeolothrips intermedius Bagnall (Thysanoptera: Aeolothripidae) and its potential prey Thysanoptera species on different cultivated host plants. J. Pest Sci. 2005, 78, 217–226. [Google Scholar] [CrossRef]
  79. Daane, K.M.; Almeida, R.P.P.; Bell, V.A.; Walker, J.T.S.; Botton, M.; Fallahzadeh, M.; Mani, M.; Miano, J.L.; Sforza, R.; Walton, V.M.; et al. Biology and management of mealybugs in vineyards. In Arthropod Management in Vineyards: Pest, Approaches, and Future Directions; Bostanian, N.J., Vincent, C., Isaac, R., Eds.; Springer Science + Business Media B.V.: Dordrecht, The Netherlands, 2012; pp. 271–307. [Google Scholar] [CrossRef]
  80. Arzone, A.; Vidano, C.; Arnò, C. Predators and parasitoids of Empoasca vitis and Zygina rhamni (Rhynchota Auchrenorrhyncha). In Proceedings of the 6th Auchenorrhyncha Meeting, Turin, Italy, 7–11 September 1987; Vidano, C., Arzone, A., Eds.; CNR-IPRA: Turin, Italy, 1988; pp. 623–629. [Google Scholar]
  81. Girolami, V.; Duso, C.; Refatti, E.; Osler, R. Lotta Integrata in Viticoltura, Malattie Della Vite; IRIPA-Coldiretti Edizioni: Treviso, Italy, 1989. [Google Scholar]
  82. Genini, M. Antagonistes de la cicadelle verte et des vers de la grappe dans le vignoble valaisan et les milieux environnants. Rev. suisse Vitic. Arboric. Hortic. 2000, 32, 153–162. [Google Scholar]
  83. Benhadi-Marín, J.; Pereira, J.A.; Santos, S.A.P. Effects of kaolin particle films on the life span of an orb-weaver spider. Chemosphere 2016, 144, 918–924. [Google Scholar] [CrossRef]
  84. Reichert, S.; Lockley, T. Spiders as biological control agents. Annu. Rev. Entomol. 1984, 29, 299–320. [Google Scholar] [CrossRef]
  85. Nyffeler, M.; Dean, D.A.; Sterling, W.L. Evaluation of the importance of the striped lynx spider, Oxyopes salticus (Araneae: Oxyopidae), as a predator in Texas cotton. Environ. Entomol. 1987, 16, 1114–1123. [Google Scholar] [CrossRef]
  86. Huseynov, E.F. Natural prey of the jumping spider Menemerus taeniatus (Araneae: Salticidae). Eur. J. Entomol. 2005, 102, 797–799. [Google Scholar] [CrossRef] [Green Version]
  87. Bengochea, P.; Amor, F.; Saelices, R.; Hernando, S.; Budia, F.; Adán, Á.; Medina, P. Kaolin and copper-based products applications: Ecotoxicology on four natural enemies. Chemosphere 2013, 91, 1189–1195. [Google Scholar] [CrossRef] [PubMed]
  88. Gharbi, N.; Abdallah, S.B. Laboratory evaluation of side-effects of kaolin on two predator species found on olive groves. Tunis. J. Plant Prot. 2016, 11, 83–90. [Google Scholar]
  89. Tacoli, F.; Bell, V.A.; Cargnus, E.; Pavan, F. Insecticidal activity of natural products against vineyard mealybugs (Hemiptera: Pseudococcidae). Crop. Prot. 2018, 111, 50–57. [Google Scholar] [CrossRef]
  90. Joubert, P.H.; Grové, T.; De Beer, M.S.; Steyn, W.P. Evaluation of kaolin (Surround® Wp) in an IPM program on mangoes in South Africa. Acta Hortic. 2004, 645, 493–499. [Google Scholar] [CrossRef]
  91. Skouras, P.J.; Stathas, G.J.; Demopoulos, V.; Louloudakis, G.; Margaritopoulos, J.T. The effect of five insecticides on the predators Coccinella septempunctata and Hippodamia variegata. Phytoparasitica 2019, 47, 197–205. [Google Scholar] [CrossRef]
  92. Bengochea, P.; Saelices, R.; Amor, F.; Adán, Á.; Budia, F.; del Estal, P.; Viñuela, E.; Medina, P. Non-target effects of kaolin and coppers applied on olive trees for the predatory lacewing Chrysoperla carnea. Biocontrol Sci. Technol. 2014, 24, 625–640. [Google Scholar] [CrossRef]
  93. Bestete, L.R.; Torres, J.B.; Pereira, F.F. Harmonious interaction of kaolin and two insect predator species in plant protection. Int. J. Pest Manag. 2018, 64, 166–172. [Google Scholar] [CrossRef]
  94. Strapazzon, A.; Pavan, F.; Cristoferi, K. Monitoraggio dei fitomizi della vite con trappole cromotropiche: Risposta di Drepanothrips reuteri Uzel al colore giallo ed alle dimensioni delle trappole. Frustula entomologica 1990, 11, 9–18. [Google Scholar]
  95. Pavan, F.; Cargnus, E.; Tacoli, F.; Zandigiacomo, P. Standardization and criticism of sampling procedures using sticky card traps: Monitoring sap-sucking insect pests and Anagrus atomus inhabiting European vineyards. Bull. Insectol. 2021, 74, 291–306. [Google Scholar]
  96. Pennington, T.; Kolb, S.; Kaiser, J.; Hoffmann, C.; Entling, M.H. Does minimal pruning and reduced fungicide use impact spiders in the grapevine canopy? J. Arachnol. 2019, 47, 381–384. [Google Scholar] [CrossRef]
  97. Legner, E.F.; Oatman, E.R. Spiders on apple in Wisconsin and their abundance in natural and two artificial environments. Can. Entomol. 1964, 96, 1202–1207. [Google Scholar] [CrossRef]
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Figure 1. Biplot of the non-metric multidimensional scaling (NMDS) ordination applied to spider communities collected by the drop cloth method in (a) Vineyard A (2015 and 2016); and in (b) Vineyards B (2015) and C (2016), respectively. Shifts in spider community under the different combinations of kaolin application and bunch-zone leaf removal (LR) are indicated by the centroids of each combination (i.e., con. no LR = control without LR, con. LR = control with LR, kaol. no LR = kaolin without LR, kaol. LR = kaolin with LR) and the standard error of the average of scores (shaded elliptic area with 95% confidence limit). A selection of species was plotted according to species scores with a further abundance priority selection. Species’ full names are reported in Table S1 of the Supplementary Materials.
Figure 1. Biplot of the non-metric multidimensional scaling (NMDS) ordination applied to spider communities collected by the drop cloth method in (a) Vineyard A (2015 and 2016); and in (b) Vineyards B (2015) and C (2016), respectively. Shifts in spider community under the different combinations of kaolin application and bunch-zone leaf removal (LR) are indicated by the centroids of each combination (i.e., con. no LR = control without LR, con. LR = control with LR, kaol. no LR = kaolin without LR, kaol. LR = kaolin with LR) and the standard error of the average of scores (shaded elliptic area with 95% confidence limit). A selection of species was plotted according to species scores with a further abundance priority selection. Species’ full names are reported in Table S1 of the Supplementary Materials.
Insects 14 00126 g001
Insects 14 00126 g002 550
Figure 2. Spiders collected by the drop cloth method in Vineyards B and C. Trends of spider diversity (Shannon index), and functional richness and evenness. No significant interactions emerged during the statistical analysis. No LR = without leaf removal, LR = with leaf removal.
Figure 2. Spiders collected by the drop cloth method in Vineyards B and C. Trends of spider diversity (Shannon index), and functional richness and evenness. No significant interactions emerged during the statistical analysis. No LR = without leaf removal, LR = with leaf removal.
Insects 14 00126 g002
Table
Table 1. Application timings of kaolin and bunch-zone leaf removal (LR), and sampling dates in 2015 for Vineyards A and B, and in 2016 for Vineyards A and C. Phenological growth stages of grapevine in BBCH-scale are reported [51].
Table 1. Application timings of kaolin and bunch-zone leaf removal (LR), and sampling dates in 2015 for Vineyards A and B, and in 2016 for Vineyards A and C. Phenological growth stages of grapevine in BBCH-scale are reported [51].
DateTimingBBCH
Vineyards A and B—2015
17 JuneLR73
18 JuneFirst kaolin spraying75
24 JuneSecond kaolin spraying75
Vineyard A—2016
10 JuneLR and First kaolin spraying71
11–19 JuneRain: about 90 mm in 8 days http://www.osmer.fvg.it/archivio.php (accessed on 20 June 2016)71–74
20 JuneSecond kaolin spraying74
28 JuneThird kaolin spraying77
Vineyard C—2016
10 JuneLR and First kaolin spraying71
24 JuneSecond kaolin spraying77
Table
Table 2. Spiders collected by the drop cloth method in Vineyard A (2015 and 2016). Effects of kaolin, bunch-zone leaf removal (LR) and time (year) and their interactions on spider diversity and functional guilds (i.e., body size and hunter percentage). The outcomes rely on the ANOVA test applied to linear mixed-effects models (LMM). Significant differences are highlighted in bold.
Table 2. Spiders collected by the drop cloth method in Vineyard A (2015 and 2016). Effects of kaolin, bunch-zone leaf removal (LR) and time (year) and their interactions on spider diversity and functional guilds (i.e., body size and hunter percentage). The outcomes rely on the ANOVA test applied to linear mixed-effects models (LMM). Significant differences are highlighted in bold.
Indices and Functional GuildsFactorsFD.F.p
Species diversity
(Shannon index H’)		Intercept63.3051, 14<0.0001
kaolin1.7901, 140.202
LR0.5361, 140.476
year0.0391, 140.847
kaolin:LR0.6111, 140.448
kaolin:year0.0501, 140.826
year:LR0.5941, 140.454
kaolin:LR:year0.4851, 140.498
Functional richnessIntercept64.7741, 14<0.0001
kaolin1.3071, 140.272
LR0.0011, 140.982
year4.0241, 140.065
kaolin:LR0.9071, 140.357
kaolin:year0.0071, 140.934
year:LR0.6811, 140.423
kaolin:LR:year1.3981, 140.257
Functional evennessIntercept25.0681, 140.000
kaolin1.9821, 140.181
LR0.1391, 140.715
year0.5871, 140.456
kaolin:LR4.0241, 140.065
kaolin:year0.0171, 140.899
year:LR0.0971, 140.760
kaolin:LR:year0.6761, 140.425
Functional distanceIntercept45.5891, 13<0.0001
kaolin0.2721, 130.611
LR0.0481, 130.830
year0.1001, 130.757
kaolin:LR1.4261, 130.254
kaolin:year1.8411, 130.198
year:LR0.2881, 130.600
kaolin:LR:year0.2881, 130.601
Body sizeIntercept92.9151, 13<0.0001
kaolin0.1811, 130.677
LR1.0391, 130.327
year0.8571, 130.372
kaolin:LR0.9521, 130.347
kaolin:year0.5161, 130.485
year:LR0.8221, 130.381
kaolin:LR:year0.1351, 130.719
log (hunter % + 0.1)Intercept4.1781, 130.062
kaolin1.3131, 130.273
LR0.0011, 130.975
year0.4051, 130.536
kaolin:LR0.0941, 130.764
kaolin:year0.0261, 130.873
year:LR1.6131, 130.226
kaolin:LR:year2.1741, 130.164
Table
Table 3. Spiders collected by the drop cloth method in Vineyard A in each of the two sampling years (2015 and 2016). For total spiders, different groups (web-builders and hunters) and families, the average number of captures per replicate throughout the sampling period (mean ± standard error) is reported. The results of ANOVA test applied to linear mixed-effects models for kaolin and bunch-zone leaf removal (LR) factors are reported. When the number of spiders collected over the whole sampling period was less than 10, no statistical analyses were carried out. Significant differences are highlighted in bold.
Table 3. Spiders collected by the drop cloth method in Vineyard A in each of the two sampling years (2015 and 2016). For total spiders, different groups (web-builders and hunters) and families, the average number of captures per replicate throughout the sampling period (mean ± standard error) is reported. The results of ANOVA test applied to linear mixed-effects models for kaolin and bunch-zone leaf removal (LR) factors are reported. When the number of spiders collected over the whole sampling period was less than 10, no statistical analyses were carried out. Significant differences are highlighted in bold.
TaxonKaolinLR
ControlKaolinFD.F.pNo LRLRFD.F.p
2015
Total spiders5.0 ± 1.43.8 ± 1.42.3081, 120.1554.4 ± 1.44.4 ± 1.40.0001, 121.000
Web-builders1.1 ± 1.01.0 ± 0.70.0341, 120.8571.3 ± 1.00.9 ± 0.70.3031, 120.592
 Araneidae0.9 ± 0.90.6 ± 0.60.5091, 120.4890.9 ± 0.60.6 ± 0.60.0571, 120.816
 Linyphiidae0.1 ± 0.30.1 ± 0.3−−−0.3 ± 0.30.0 ± 0.0−−−
 Theridiidae0.1 ± 0.30.3 ± 0.3−−−0.1 ± 0.30.3 ± 0.3−−−
Hunters3.9 ± 1.32.8 ± 1.43.5221, 120.0853.1 ± 1.33.5 ± 1.40.3911, 120.543
 Thomisidae1.8 ± 1.02.1 ± 1.20.3701, 120.5541.9 ± 1.12.0 ± 1.10.0411, 120.843
 Gnaphosidae0.3 ± 0.30.3 ± 0.3− 0.3 ± 0.30.3 ± 0.3−−−
 Oxyopidae1.5 ± 1.10.1 ± 0.36.1531, 120.0290.5 ± 0.51.1 ± 1.01.2711, 120.282
 Salticidae0.4 ± 0.40.3 ± 0.5−−−0.5 ± 0.60.1 ± 0.3−−−
2016
Total spiders4.4 ± 1.63.8 ± 1.60.3111, 120.5873.3 ± 1.64.9 ± 1.62.1041, 120.173
Web-builders1.4 ± 0.90.9 ± 0.70.8891, 120.3640.9 ± 0.81.4 ± 0.80.8891, 120.364
 Araneidae1.1 ± 0.60.3 ± 0.37.0001, 120.0210.5 ± 0.50.9 ± 0.61.2861, 120.279
 Linyphiidae0.3 ± 0.30.5 ± 0.5−−−0.4 ± 0.40.4 ± 0.4−−−
 Theridiidae0.0 ± 0.00.1 ± 0.3−−−0.0 ± 0.00.1 ± 0.3−−−
Hunters3.0 ± 1.62.9 ± 1.70.0141, 120.9082.4 ± 1.43.5 ± 1.81.1201, 120.311
 Thomisidae1.1 ± 1.02.3 ± 1.42.5051, 120.1391.1 ± 0.82.3 ± 1.52.5051, 120.139
 Gnaphosidae0.1 ± 0.30.3 ± 0.3−−−0.1 ± 0.30.3 ± 0.3−−−
 Miturgidae0.1 ± 0.30.0 ± 0.0−−−0.0 ± 0.00.1 ± 0.3−−−
 Oxyopidae0.3 ± 0.30.0 ± 0.0−−−0.1 ± 0.30.1 ± 0.3−−−
 Salticidae1.3 ± 0.80.3 ± 0.35.6471, 120.0350.9 ± 0.70.6 ± 0.50.0631, 120.563
 Sparassidae0.1 ± 0.30.1 ± 0.3−−−0.1 ± 0.30.1 ± 0.3−−−
Table
Table 4. Insects and spiders captured with yellow sticky traps in Vineyard A in 2015. For total spiders and their groups (web-builders and hunters), and taxa of insects and spiders, the average number of captures per trap throughout the sampling period (mean ± standard error) is reported. The results of ANOVA test applied to linear mixed-effects models for kaolin and bunch-zone leaf removal (LR) factors are reported. Significant differences are highlighted in bold.
Table 4. Insects and spiders captured with yellow sticky traps in Vineyard A in 2015. For total spiders and their groups (web-builders and hunters), and taxa of insects and spiders, the average number of captures per trap throughout the sampling period (mean ± standard error) is reported. The results of ANOVA test applied to linear mixed-effects models for kaolin and bunch-zone leaf removal (LR) factors are reported. Significant differences are highlighted in bold.
TaxonKaolinLR
ControlKaolinFD.F.pNo LRLRFD.F.p
Insects
Aeolothrips sp.59.6 ± 10.571.0 ± 20.20.4441, 120.51838.0 ± 8.492.6 ± 15.610.2301, 120.008
Scymninae3.1 ± 0.56.4 ± 1.08.3801, 120.0133.9 ± 10.95.6 ± 1.12.4301, 120.145
Coccinellidae non Scymninae3.9 ± 0.62.8 ± 0.61.8271, 120.2012.6 ± 0.64.0 ± 0.62.7291, 120.124
Chrysoperla carnea s.l.2.3 ± 0.691.0 ± 0.43.0001, 120.1091.8 ± 0.41.5 ± 0.70.120 1, 120.735
Orius sp.2.6 ± 0.81.0 ± 0.33.5961, 120.0822.4 ± 0.71.3 ± 0.61.723 1, 120.214
Spiders
Total15.8 ± 2.512.5 ± 1.41.2571, 120.28412.4 ± 21.515.9 ± 2.41,4571, 120.251
Web-builders6.6 ± 1.35.0 ± 0.51.3171, 120.2744.8 ±0.56.9 ± 1.32.2521, 120.159
Hunters9.1 ± 1.47.5 ± 1.20.7191, 120.4137.6 ± 1.39.0 ± 1.30.5151, 120.487
 Thomisidae4.9 ± 1.03.6 ± 0.71.1811, 120.2983.1 ± 0.75.4 ± 1.93.8271, 120.074
 Gnaphosidae0.4 ± 0.30.3 ± 0.20.1761, 120.6820.1 ± 0.10.5 ± 0.31.5881, 120.232
 Oxyopidae0.5 ± 0.30.9 ± 0.40.5741, 120.4630.5 ± 0.30.9 ± 0.40.5741, 120.463
 Salticidae3.4 ± 0.92.0 ± 0.81.4351, 120.2543.4 ± 0.92.0 ± 0.71.4351, 120.254
Table
Table 5. Spiders collected by the drop cloth method in the two Vineyards B (2015) and C (2016). Effects of kaolin, bunch-zone leaf removal (LR) and vineyard and their interactions on spider diversity and functional guilds (i.e., body size and hunter percentage). The outcomes rely on the ANOVA test applied to linear mixed-effects models. Significant differences are highlighted in bold.
Table 5. Spiders collected by the drop cloth method in the two Vineyards B (2015) and C (2016). Effects of kaolin, bunch-zone leaf removal (LR) and vineyard and their interactions on spider diversity and functional guilds (i.e., body size and hunter percentage). The outcomes rely on the ANOVA test applied to linear mixed-effects models. Significant differences are highlighted in bold.
Indices and Functional GuildsFactorsFD.F.p
Species diversity
(Shannon index H’)		Intercept176.9401, 14<0.0001
kaolin1.8801, 140.192
LR6.1711, 140.026
year19.1291, 140.001
kaolin:LR0.0161, 140.902
kaolin:year0.1671, 140.689
year:LR1.8111, 140.200
kaolin:LR:year3.1431, 140.098
Functional richnessIntercept155.7921, 13<0.0001
kaolin0.0681, 130.798
LR1.9031, 130.191
year9.9581, 130.008
kaolin:LR2.1151, 130.170
kaolin:year0.0081, 130.928
year:LR0.0251, 130.877
kaolin:LR:year0.4131, 130.532
Functional evennessIntercept85.3791, 14<0.0001
kaolin0.3121, 140.585
LR7.8181, 140.014
year7.0941, 140.019
kaolin:LR2.3891, 140.145
kaolin:year1.0061, 140.333
year:LR2.8451, 140.114
kaolin:LR:year0.9851, 140.338
Functional distanceIntercept133.8341, 13<0.0001
kaolin0.2241, 130.644
LR2.9451, 130.110
year4.4931, 130.054
kaolin:LR0.0381, 130.849
kaolin:year0.0131, 130.913
year:LR0.5661, 130.465
kaolin:LR:year0.3771, 130.550
Body sizeIntercept172.1781, 13<0.0001
kaolin1.3321, 130.269
LR3.6461, 130.079
year0.8381, 130.377
kaolin:LR0.0021, 130.968
kaolin:year0.2701, 130.612
year:LR0.4411, 130.518
kaolin:LR:year0.0221, 130.886
log (hunter % + 0.1)Intercept18.9151, 130.001
kaolin0.0551, 130.818
LR0.1541, 130.701
year2.9161, 130.112
kaolin:LR1.7621, 130.207
kaolin:year0.4831, 130.499
year:LR2.8051, 130.118
kaolin:LR:year1.4081, 130.257
Table
Table 6. Spiders collected by the drop cloth method in the two Vineyards B (2015) and C (2016). For total spiders, different groups (web-builders and hunters) and families, the average number of captures per replicate throughout the sampling period (mean ± standard error) is reported. The results of ANOVA test applied to linear mixed-effects models for kaolin and bunch-zone leaf removal (LR) factors are reported. When the number of spiders collected over the whole sampling period was less than 10, no statistical analyses were carried out.
Table 6. Spiders collected by the drop cloth method in the two Vineyards B (2015) and C (2016). For total spiders, different groups (web-builders and hunters) and families, the average number of captures per replicate throughout the sampling period (mean ± standard error) is reported. The results of ANOVA test applied to linear mixed-effects models for kaolin and bunch-zone leaf removal (LR) factors are reported. When the number of spiders collected over the whole sampling period was less than 10, no statistical analyses were carried out.
TaxonKaolinLR
ControlKaolinFD.F.pNo LRLRFD.F.p
Vineyard B
Total spiders9.9 ± 2.410.1 ± 3.00.0291, 120.86810.4 ± 32.49.6 ± 3.00.2611, 120.619
Web-builders3.8 ± 1.43.9 ± 2.00.0141, 120.9074.1 ± 1.83.5 ± 1.70.3521, 120.564
 Araneidae2.5 ± 1.31.5 ± 1.20.5911, 120.4572.3 ± 1.21.8 ± 1.20.0241, 120.880
 Linyphiidae0.9 ± 0.81.6 ± 1.50.5911, 120.4571.3 ± 1.41.3 ± 1.00.0001, 121.000
 Theridiidae0.4 ± 0.40.8 ± 0.80.0001, 121.0000.6 ± 0.60.5 ± 0.60.6671, 120.430
Hunters6.1 ± 2.16.3 ± 2.20.0091, 120.9266.3 ± 2.16.1 ± 2.30.0091, 120.926
 Thomisidae2.9 ± 1.73.8 ± 2.20.4521, 120.5143.1 ± 1.73.5 ± 2.10.0831, 120.778
 Gnaphosidae0.5 ± 0.71.0 ± 0.90.5581, 120.4690.9 ± 0.80.6 ± 0.80.1401, 120.715
 Oxyopidae1.4 ± 1.11.0 ± 0.70.2521, 120.6251.0 ± 0.81.4 ± 1.10.2521, 120.625
 Salticidae0.9 ± 0.90.5 ± 0.50.3251, 120.5790.8 ± 10.80.6 ± 0.60.0361, 120.852
 Sparassidae0.5 ± 0.60.0 ± 0.0−−−0.5 ± 0.60.0 ± 0.0−−−
Vineyard C
Total spiders4.4 ± 1.23.1 ± 1.42.7931, 120.1213.9 ± 1.33.6 ± 1.30.3101, 120.588
Web-builders1.8 ± 0.91.4 ± 0.90.4741, 120.5041.5 ± 0.91.6 ± 0.90.0531, 120.822
 Araneidae1.3 ± 0.80.9 ± 0.50.6921, 120.4221.0 ± 0.61.1 ± 0.70.0771, 120.786
 Linyphiidae0.5 ± 0.60.5 ± 0.5−−−0.5 ± 0.50.5 ± 0.6−−−
Hunters2.6 ± 1.01.8 ± 0.91.8621, 120.1972.4 ± 1.02.0 ± 1.00.8281, 120.381
 Thomisidae0.4 ± 0.40.3 ± 0.3−−−0.1 ± 0.30.5 ± 0.5−−−
 Gnaphosidae0.0 ± 0.00.1 ± 0.3−−−0.1 ± 0.30.0 ± 0.0−−−
 Miturgidae0.1 ± 0.30.0 ± 0.0−−−0.0 ± 0.00.1 ± 0.3−−−
 Oxyopidae1.0 ± 0.70.6 ± 0.51.0801, 120.3190.9 ± 0.60.8 ± 0.70.1201, 120.735
 Salticidae1.1 ± 0.70.8 ± 0.80.1761, 120.6821.3 ± 1.00.6 ± 0.51.5881, 120.232
Table
Table 7. Insects and spiders captured with yellow sticky traps in Vineyard B in 2015. For total spiders and their groups (web-builders and hunters), and taxa of insects and spiders, the average number of captures per trap throughout the sampling period (mean ± standard error) is reported. The results of ANOVA test applied to linear mixed-effects models for kaolin and bunch-zone leaf removal (LR) factors are reported. Significant differences are highlighted in bold.
Table 7. Insects and spiders captured with yellow sticky traps in Vineyard B in 2015. For total spiders and their groups (web-builders and hunters), and taxa of insects and spiders, the average number of captures per trap throughout the sampling period (mean ± standard error) is reported. The results of ANOVA test applied to linear mixed-effects models for kaolin and bunch-zone leaf removal (LR) factors are reported. Significant differences are highlighted in bold.
TaxonKaolinLR
ControlKaolinFD.F.pNo LRLRFD.F.p
Insects
Aeolothrips sp.55.6 ± 12.492.5 ± 21.22.0201, 120.18164.5 ± 19.083.6 ± 17.70.5431, 120.475
Scymninae5.9 ± 6.99.5 ± 8.72.4221, 120.14616.3 ± 3.122.1 ± 5.21.0611, 120.323
Coccinellidae non-Scymninae6.8 ± 1.48.4 ± 1.30.6101, 120.4507.3 ± 1.67.9 ± 1.20.0901, 120.769
Chrysoperla carnea s.l.2.6 ± 0.92.0 ± 0.50.3161, 120.5841.9 ± 0.82.8 ± 0.60.6201, 120.446
Orius sp.3.0 ± 0.80.9 ± 0.45.0701, 120.0442.1 ± 0.91.8 ± 0.50.1581, 120.698
Spiders
Total spiders19.4 ± 2.820.8 ± 2.90.1041, 120.75319.1 ± 3.321.0 ± 2.30.1931, 120.668
Web-builders7.1 ± 1.48.8 ± 1.50.4971, 120.4947.6 ± 2.08.3 ± 1.00.0731, 120.791
Hunters12.2 ± 2.212.0 ± 1.60.0081, 120.93111.5 ± 31.712.8 ± 2.10.1941, 120.668
 Thomisidae6.1 ± 2.06.4 ± 1.00.0111, 120.9185.9 ± 1.26.6 ± 1.90.0991, 120.758
 Gnaphosidae1.0 ± 0.30.5 ± 0.31.7141, 120.2150.8 ± 0.30.8 ± 0.30.0001, 121.000
 Oxyopidae2.0 ± 0.62.5 ± 0.70.2891, 120.6012.4 ± 0.82.1 ± 0.40.0721, 120.793
 Salticidae3.0 ± 0.82.5 ± 0.70.2111, 120.6552.3 ± 0.83.3 ± 0.70.8421, 120.377
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Cargnus, E.; Tacoli, F.; Boscutti, F.; Zandigiacomo, P.; Pavan, F. Side Effects of Kaolin and Bunch-Zone Leaf Removal on Generalist Predators in Vineyards. Insects 2023, 14, 126. https://doi.org/10.3390/insects14020126

AMA Style

Cargnus E, Tacoli F, Boscutti F, Zandigiacomo P, Pavan F. Side Effects of Kaolin and Bunch-Zone Leaf Removal on Generalist Predators in Vineyards. Insects. 2023; 14(2):126. https://doi.org/10.3390/insects14020126

Chicago/Turabian Style

Cargnus, Elena, Federico Tacoli, Francesco Boscutti, Pietro Zandigiacomo, and Francesco Pavan. 2023. "Side Effects of Kaolin and Bunch-Zone Leaf Removal on Generalist Predators in Vineyards" Insects 14, no. 2: 126. https://doi.org/10.3390/insects14020126

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