Research Article |
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Corresponding author: Simona Dumitrița Chirilă ( simonachirilasc@yahoo.com ) Academic editor: Olivier Chabrerie
© 2026 Simona Dumitrița Chirilă, Alexandru-Mihai Pintilioaie, Ana Mariana Chirilă, Nikolay Velev.
This is an open access article distributed under the terms of the Creative Commons Attribution License (CC BY 4.0), which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
Citation:
Chirilă SD, Pintilioaie A-M, Chirilă AM, Velev N (2026) Relationship between the morphology of Crambe tataria and the functional groups of insects in northeastern Romania. Plant Ecology and Evolution 159(2): 295-309. https://doi.org/10.5091/plecevo.169013
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Background and aims – The relationships between insect species and plant functional traits are complex but vital in their ecosystem structure and functioning. Our study examined functional traits of Crambe tataria to assess their influence on insect abundance and community composition.
Material and methods – The study was carried out in April–May 2024 and 2025 at four locations in Iași and Vaslui counties, Romania. We investigated the presence of insects on C. tataria inflorescences and their relationship to plant functional traits. To understand the relationships between plant functional traits (plant height and inflorescence circumference) and insect abundance, we applied a Kendall’s rank correlation test. The vegetation was classified using agglomerative hierarchical clustering, while insect community clustering was based on Euclidean distances and complete linkage.
Key results – A total of 36 insect taxa were identified on C. tataria, including 30 taxa identified to species level and six identified only to the genus level. The predominant trophic group was represented by phytophagous insects. Rare or conservation-relevant species, such as Clanoptilus affinis and Lixus canescens, were also recorded. A positive correlation was found between plant height and the number of Cercopis sanguinolenta. The number of C. sanguinolenta, Eurydema ornata, and Bibio hortulanus significantly increased with inflorescence circumference. Cluster analyses (108 plots) revealed three plant associations and three distinct insect communities, mainly phytophagous or pollen-feeding. Alpha-diversity indices varied between locations: Horlești presented the highest richness, Miroslava and Vulturi presented moderate diversity, while Glodeni had lower diversity. The PERMANOVA test showed that plant height and inflorescence circumference in C. tataria significantly influenced the composition of the insect community, explaining 34.5% of the observed variation.
Conclusion – Plant height and inflorescence circumference of C. tataria were significantly correlated with the abundance of some phytophagous insect species, particularly Cercopis sanguinolenta, Eurydema ornata, and Bibio hortulanus.
Crambe tataria, plant-insect interactions, insect communities, alpha diversity, steppe grasslands
Plant-insect relationships are continuously changing (
Grasslands play a central role in maintaining biodiversity, as they support a high diversity of plant and animal species. Within these grasslands, steppe relict habitats play a critical role in maintaining biodiversity and supporting food webs (
Crambe tataria is characteristic of the following Natura 2000 habitats (
Interactions with insects are important for understanding the ecology of some species (
Crambe tataria exhibits an active glucosinolate-myrosinase system, identified in the seeds and leaves of in vivo- and in vitro-regenerated seedlings as well as in two callus cell lines (
There are no published studies on pollination in C. tataria. However, other Crambe species are insect-pollinated, with bees (Hymenoptera) documented as key visitors in C. abyssinica Hochst. ex R.E.Fr. (
Local microclimatic factors (temperature, humidity, wind) are influenced by topography (
This study investigates some of the interactions between C. tataria and insect communities across four locations in the Moldova region of Romania. For the first time, we identify some of the insect species associated with this plant and assess its impact on the diversity and abundance of local insect fauna. At the same time, this research contributes to biodiversity management strategies in areas affected by environmental change and anthropization. Moreover, the study is important for understanding plant-insect interactions, which, in turn, can form a basis for developing various strategies aimed at conserving rare plant and insect species.
Plant height determines floral visibility and insect accessibility within the vegetation (
The study was conducted in the northeastern part of Romania, in the Moldova region, including locations in Iași County (Horlești, Miroslava, and Vulturi) and Vaslui County (Glodeni) (Fig.
During April–May 2024 and 2025, 125 individuals of C. tataria (Fig.
For the vegetation analysis, 108 plots (including 102 taxa; Suppl. material
Vegetation data were represented by the mean percentage values of the
Vegetation classification was performed using the Agglomerative Hierarchical Clustering (ß-flexible method, ß = -0.25 and Bray-Curtis dissimilarity). The dendrogram was created using the GINKGO program from the VegAna package (
The EUNIS habitat type was identified using the EUNIS habitat expert classification system (
Data on the number of insect species and individuals were collected from each vegetative or flowering C. tataria individual included in our study (Suppl. material
For each individual plant, insects were sampled using a standard protocol. All insects present on leaves, stems, buds, and inflorescences were recorded. Each plant was inspected for 3–5 minutes, during which time insects were collected directly by hand, using a hand net or an entomological pooter. The protocol targeted all insects interacting directly with the plant surface. As the insect species are most of the time hard or impossible to identify in the field, given the high diversity of (apparently) similar species and their small size, most of the individuals observed were collected, in order to be carefully determined in the laboratory.
All the observed insects were collected except for three species – Carpocoris purpureipennis, Cercopis sanguinolenta, and Tropinota (Epicometis) hirta – from which only a subset of individuals was sampled due to their high field abundance and the ease of assigning them to genus in situ. The collected individuals of these three genera were identified to species level in the laboratory, and this information was subsequently used to update the field records, assigning species-level identifications to all specimens initially recorded only at the genus level. One Carpocoris specimen remained unidentified to species level because it was fragmented and thus lacked the diagnostic characters required for identification. The specimens were identified as precisely as possible and deposited in the personal collection of Pintilioaie Alexandru-Mihai, housed in Agigea, Romania. Following this, each taxon was classified in terms of the trophic preferences of the adults into three categories: phytophagous insects (Ph), predatory insects (Pr), and omnivorous insects (Om). The scientific names given in the table are in accordance with
Predatory insects (Pr) were included in this study because they reflect the local trophic structure and may indirectly influence the pressure exerted by phytophagous insects on C. tataria. It should also be noted that a distinct group of pollinators was not defined, as very few floral visitors were observed. Thus, the majority belonged to taxa that can act both as phytophagous species and as occasional pollen feeders.
Cluster analyses for entomofauna were performed in the GINKGO software (
Statistical analyses were limited to seven highly abundant insect species: Tropinota (Epicometis) hirta – 566 individuals, Cercopis sanguinolenta – 237 individuals, Carpocoris purpureipennis – 77 individuals, Bibio hortulanus – 15 individuals, Eurydema ornata – 13 individuals, Camponotus piceus – 11 individuals, and Dolycoris baccarum – nine individuals, which allowed the application of non-parametric tests. Linear regressions were used as descriptive tools only, and inferential analysis was based on the Kendall’s tau test.
We calculated the alpha-diversity indices, including Shannon, Simpson (1–D), Pielou’s evenness, and Chao1, to characterize the insect diversity within the four sampled areas. We estimated the main effect of two functional plant traits (inflorescence circumference and plant height) on insect species composition using the non-parametric PERMANOVA test based on the Bray-Curtis distance matrix. Along with PERMANOVA, we tested homogeneity of multivariate dispersions (variance) using the betadisper function of the R package vegan v.2.8-0. The correlation between insect abundance and the two plant traits was explored by Kendall’s tau correlation. Statistical analyses were performed in R v.4.1.4 (
Crambe tataria was recorded in three plant associations (Fig.
The diagnostic species were Elytrigia repens (IndVal = 0.980, p < 0.01), Teucrium chamaedrys L. (IndVal = 0.700, p < 0.05), Vicia tenuifolia Roth (IndVal = 0.559, p < 0.05), and Salvia austriaca Jacq. (IndVal = 0.509, p < 0.05).
In plots included in this cluster, Elytrigia repens predominated, which forms the Rorippo austriacae-Agropyretum repentis association. This association belongs to the alliance Potentillion anserinae Tx. 1947, within the order Potentillo-Polygonetalia avicularis Tx. 1947, and the class Molinio-Arrhenatheretea Tx. 1937.
Communities with E. repens were classified in the EUNIS habitat R36 Moist or wet mesotrophic to eutrophic pasture.
The association was recorded in some locations in Iași County, at moderate elevations (from 132 to 141 m a.s.l.), on steep slopes (from 8 to 21°) with northern and northwest aspect. Crambe tataria individuals show morphological differences between vegetative and flowering plants. Vegetative individuals had an average of ten leaves per plant, a height of 39–45 cm. Flowering individuals were leafless, a height of 94 cm, and had an inflorescence circumference of 223 cm.
The entomofauna was dominated by phytophagous species, the most numerous being Tropinota (Epicometis) hirta, with up to 27 individuals per plot, and Cercopis sanguinolenta, with a maximum of 65 individuals. In the case of Carpocoris purpureipennis, up to 16 individuals were recorded, and Eurydema ornata and Coriomeris denticulatus were recorded sporadically. Omnivorous and predatory species are poorly represented. Isolated ant species (Camponotus piceus, C. aethiops, and Formica cunicularia) were observed, with a maximum of two individuals per plot. Predatory species of the type Orius sp. and Lygaeus sp. were identified very rarely. The same pattern of the entomofauna was observed in both vegetative and flowering C. tataria individuals. The abundance was higher on flowering plants.
The diagnostic species were Stipa lessingiana (IndVal = 0.977, p < 0.01), Salvia nemorosa L. (IndVal = 0.670, p < 0.05), and Stachys recta L. (IndVal = 0.663, p < 0.05).
The plots included in cluster 2 were characterized by the dominance of the species Stipa lessingiana, which forms the association Jurineo arachnoideae-Stipetum lessingianae. This association belongs to the alliance Stipion lessingianae Soó 1947, within the order Festucetalia valesiacae Soó 1947, and the class Festuco-Brometea Br.-Bl. et Tx. ex Soó 1947. This cluster corresponds to the continental steppe communities, classified in EUNIS R1B Continental dry grasslands (true steppe). In terms of Natura 2000 habitats, the investigated communities are associated with Habitat 62C0* Ponto-Sarmatic steppes.
Stipa lessingiana communities were recorded in locations in Iași and Vaslui counties, at higher elevations than cluster 1 (from 137 to 201 m a.s.l.), on steep slopes (from 11 to 30°) with southwest, west and south aspects.
Crambe tataria individuals were well-developed, with heights exceeding 80 cm and inflorescence circumferences over 204 cm. No leaves were observed on flowering individuals.
The entomofauna was dominated by phytophagous species, but with a lower diversity and abundance compared to cluster 1. The most frequent insect species were Tropinota (Epicometis) hirta, in which five individuals were recorded, and Cercopis sanguinolenta, with nine individuals. Also, three individuals of Protaetia (Philhelena) ungarica and two individuals of Carpocoris purpureipennis were recorded. Omnivorous species were few, being represented by Camponotus piceus with one individual. Dolycoris baccarum was observed only once, and Melanobaris carbonaria was also recorded with a single individual.
The diagnostic species was Festuca valesiaca Schleich. ex Gaudin (IndVal = 0.976, p < 0.01).
Cluster 3 was dominated by Festuca valesiaca, which is the characteristic species for the Taraxaco serotinae-Festucetum valesiacae association. This association belongs to the alliance Stipion lessingianae Soó 1947, within the order Festucetalia valesiacae Soó 1947, and the class Festuco-Brometea Br.-Bl. et Tx. ex Soó 1947.
Festuca valesiaca communities are characteristic of continental steppe grasslands, being classified in the EUNIS habitat R1B Continental dry grasslands (true steppe), and according to the Natura 2000 classification, the investigated communities correspond to the habitat 62C0* Ponto-Sarmatian steppes.
The association in this cluster was observed in grasslands from Iași and Vaslui counties, at relatively low elevation (from 132 to 139 m a.s.l.), on steep slopes (from 11 to 21°) with a northern and northwestern aspect. The average number of leaves per plant was five in flowering individuals and seven in vegetative individuals. The height of the plants ranged from 26 to 116 cm, likely reflecting variation in light availability and local soil moisture within the microhabitat. The inflorescence circumference has a large amplitude, with values ranging from 82 to 420 cm.
The entomofauna associated with this cluster is dominated by phytophagous species, of which Tropinota (Epicometis) hirta has the highest number of records. Cercopis sanguinolenta (from 2 to 225) and Carpocoris purpureipennis (from 1 to 38) were constantly present, with a moderate to high number of individuals. Omnivorous and predatory species, such as Formica cunicularia, appear rarely and in small numbers. Pollinating species, such as Andrena flavipes, were observed only as isolated individuals.
The insect communities associated with C. tataria were grouped into three clusters (Fig.
A small number of floral visitors were recorded on C. tataria, such as Apis mellifera and Andrena flavipes. Although rare, these insect species confirm that C. tataria is visited by potential pollinators, but their low abundance did not allow statistical analysis.
In this cluster, the entomofauna was dominated by phytophagous species, with Cercopis sanguinolenta present in several plots. Other Hemiptera species were occasionally recorded (Carpocoris purpureipennis, Dolycoris baccarum, and Eurydema ornata), without becoming dominant. Tropinota (Epicometis) hirta and Valgus hemipterus were only observed in plots with larger inflorescence circumferences of C. tataria. For Andrena flavipes (four individuals), Apis mellifera (two individuals), Camponotus piceus (11 individuals), C. aethiops (two individuals), Melanobaris carbonaria (one individual), and Teucriogethes distinctus (eight individuals), only a few individuals were recorded, all of them being associated with plants bearing inflorescences.
Cluster B was characterized by the high abundance of Cercopis sanguinolenta (Hemiptera: Cercopidae). The species had densities of 65 to 71 individuals per plot on the inflorescences of C. tataria. The high density of C. sanguinolenta individuals was recorded on plants with large inflorescences (with a circumference from 290 to 295 cm) and greater height (from 111 to 125 cm). Other insect species, such as Coccinella septempunctata and Camponotus piceus, were also recorded, but in much lower numbers.
Cluster C was characterized by Tropinota (Epicometis) hirta (Coleoptera: Cetoniidae), which had very high densities of individuals on C. tataria inflorescences. Tropinota (Epicometis) hirta reached very high densities on C. tataria, and was most frequently recorded on plants with large inflorescences (circumference 182–280 cm) and intermediate plant height (69–99 cm). Species such as Carpocoris purpureipennis, Spermophagus sericeus, Teucriogethes distinctus, and Bibio hortulanus were rarely observed. However, we currently lack sufficient field data to determine whether their low abundance is related to the phenology of their host plants species.
The insects identified on the C. tataria specimens have a diversified pattern, being dominated by certain orders (Table
| Order | Family | Species | Individuals | |||
| No. | % | No. | % | No. | % | |
| Coleoptera | 8 | 40 | 12 | 40 | 602 | 61 |
| Diptera | 2 | 10 | 2 | 7 | 17 | 2 |
| Hemiptera | 5 | 25 | 9 | 30 | 343 | 35 |
| Hymenoptera | 3 | 15 | 5 | 17 | 22 | 2 |
| Lepidoptera | 1 | 5 | 1 | 3 | 1 | 0.1 |
| Orthoptera | 1 | 5 | 1 | 3 | 1 | 0.1 |
Horlești recorded the highest species richness (15 species; Table
According to the data collected in the field, phytophagous insects (Ph) were dominant. This trophic group represents the largest proportion of the total number of insects studied. Since the pollinating species were very few in number and present in small numbers, they were treated within the Ph group. The omnivorous species (Om) is rare or absent in some locations. Regarding predatory species (Pr), they are in relatively low proportions in the analysed locations (Table
| Trophic group | Horlești | Miroslava | Vulturi | Glodeni | ||||
|---|---|---|---|---|---|---|---|---|
| No. | % | No. | % | No. | % | No. | % | |
| Om, omnivorous insects | 2 | 13 | 0 | 0 | 2 | 13 | 1 | 7 |
| Ph, phytophagous insects | 12 | 80 | 9 | 90 | 11 | 73 | 12 | 86 |
| Pr, predatory insects | 1 | 7 | 1 | 10 | 2 | 13 | 1 | 7 |
Across all analysed locations, a decrease in the diversity of predatory insect species was observed. One species (Coccinella septempunctata) was recorded in Glodeni, Horlești, and Miroslava, and two species (Coccinella septempunctata and Phymata crassipes) from this group were recorded in Vulturi. In terms of the number of individuals, the highest values were found in Glodeni and Vulturi, and the lowest in Horlești and Miroslava. The phytophagous insects were dominant in all locations, both in terms of diversity and abundance. Thus, the highest diversity and abundance were recorded in Glodeni. Moderate species richness and moderate number of individuals were recorded in Horlești, Vulturi, and Miroslava. Omnivorous insect species were recorded only in Horlești, Vulturi, and Glodeni.
Miroslava was characterized by moderate insect diversity with uneven species distribution. Glodeni exhibited low observed diversity (Shannon and Simpson), whereas the Chao1 estimator suggested a higher underlying species richness, implying the likely presence of additional undetected species. At Horlești, the highest overall insect species richness was observed, and the Chao1 index suggested that even many more species would be found here. Vulturi was characterized by an average insect diversity with Chao1 index very close to the observed value (Table
| Location | Shannon | Simpson | Pielou’s | Chao Index | ||
| Observed | Chao1 | SE_Chao1 | ||||
| Miroslava | 0.97 | 0.45 | 0.42 | 10.00 | 13.00 | 4.13 |
| Glodeni | 0.65 | 0.22 | 0.23 | 17.00 | 31.00 | 13.15 |
| Horlești | 1.97 | 0.75 | 0.64 | 22.00 | 48.25 | 18.74 |
| Vulturi | 0.74 | 0.26 | 0.27 | 15.00 | 16.67 | 2.20 |
The PERMANOVA test (p = 0.001) indicated that inflorescence circumference and plant height of C. tataria are significantly associated with changes in insect species composition. The effect size (R2) explains some 34.5% of the total variation in the insect species composition. The homogeneity of dispersion test for the two plant traits (plant height, p < 0.001; inflorescence circumference, p = 0.002) was also significant. This means that the insect species composition, to some extent, is also driven by heterogeneous dispersion, which implies that variable and unpredictable insect communities also exist (Tables
| Source variability | d.f. | Sum of Squares | R² | F value | Pr (>F) | Signif. |
| Model | 11 | 10.377 | 0.34486 | 3.3976 | 0.001 | *** |
| Residual | 71 | 19.714 | 0.65514 | |||
| Total | 82 | 30.091 | 1 |
| Source variability | d.f. | Sum of Squares | Mean Sq | F value | Pr (>F) | Signif. |
| Groups | 10 | 3.0949 | 0.309487 | 7.6148 | 3.71E-08 | *** |
| Residual | 72 | 2.9263 | 0.040643 |
| Source variability | d.f. | Sum of Squares | Mean Sq | F value | Pr (>F) | Signif. |
| Groups | 1 | 0.2403 | 0.240295 | 10.194 | 0.002007 | ** |
| Residual | 81 | 1.9094 | 0.023572 |
The relationship between inflorescence circumference and the presence of the species Dolycoris baccarum, Carpocoris purpureipennis, Camponotus piceus, and Tropinota (Epicometis) hirta is not statistically significant, while the presence of the species Bibio hortulanus (p = 0.0091), Eurydema ornata (p = 0.029), and Cercopis sanguinolenta (p = 0.027) is significantly and positively correlated with inflorescence circumference (Table
Kendall test results for the relationship between the functional traits of Crambe tataria and the associated insect species. Statistically significant relationships are in bold.
| Plant height | Inflorescence circumference | |||||
| z value | p value | Kendall’s Tau (τ) | z value | p value | Kendall’s Tau (τ) | |
| Bibio hortulanus | 1.5929 | 0.1112 | 0.1289 | 2.6082 | 0.009101 | 0.211 |
| Camponotus piceus | 0.17072 | 0.8644 | 0.0139 | 0.40975 | 0.682 | 0.0333 |
| Carpocoris purpureipennis | -1.2014 | 0.2296 | -0.0948 | 1.7462 | 0.08078 | 0.1377 |
| Cercopis sanguinolenta | 3.3349 | 0.000853 | 0.2623 | 2.2137 | 0.02685 | 0.174 |
| Dolycoris baccarum | 0.36805 | 0.7128 | 0.0302 | 1.075 | 0.2824 | 0.0881 |
| Eurydema ornata | -0.09461 | 0.9246 | -0.0077 | 2.1872 | 0.02872 | 0.1774 |
| Tropinota hirta | -0.31826 | 0.7503 | -0.0234 | -0.37641 | 0.7066 | -0.0276 |
The relationship between plant height of C. tataria and the presence of Bibio hortulanus, Camponotus piceus, Carpocoris purpureipennis, Dolycoris baccarum, Eurydema ornata, and Tropinota (Epicometis) hirta is not statistically significant. In contrast, the relationship between plant height and Cercopis sanguinolenta is statistically significant and positively correlated (Table
Despite the limited data on insect assemblages associated with C. tataria due to the short duration of fieldwork, it still provides significant insights into species diversity and their interactions with the plant. We identified 30 different taxa to species level and six of them to genus level (Table
The insect species identified in this study. Individuals only identified at the genus level were not included in the statistics.
| Insect | Order | Family | Trophic group | Location | |||
| Miroslava | Glodeni | Horlești | Vulturi | ||||
| Andrena flavipes Panzer, 1799 | Hymenoptera | Andrenidae | phytophagous | 0 | 1 | 1 | 2 |
| Apis mellifera Linnaeus, 1758 | Hymenoptera | Apidae | phytophagous | 0 | 0 | 0 | 2 |
| Bibio hortulanus (Linnaeus, 1758) | Diptera | Bibionidae | phytophagous | 0 | 14 | 1 | 0 |
| Camponotus aethiops (Latreille, 1798) | Hymenoptera | Formicidae | omnivore | 0 | 0 | 0 | 2 |
| Camponotus piceus (Leach, 1825) | Hymenoptera | Formicidae | omnivore | 0 | 0 | 4 | 7 |
| Carcharodus alceae (Esper, 1780) | Lepidoptera | Hesperiidae | phytophagous | 0 | 1 | 0 | 0 |
| Carpocoris purpureipennis (De Geer, 1773) | Hemiptera | Pentatomidae | phytophagous | 38 | 1 | 30 | 8 |
| Cercopis sanguinolenta (Scopoli, 1763) | Hemiptera | Cercopidae | phytophagous | 10 | 0 | 2 | 225 |
| Cidnopus pilosus (Leske, 1785) | Coleoptera | Elateridae | phytophagous | 0 | 0 | 4 | 0 |
| Clanoptilus (Clanoptilus) affinis (Ménétriés, 1832) | Coleoptera | Melyridae | phytophagous | 0 | 0 | 0 | 1 |
| Coccinella (Coccinella) septempunctata (Linnaeus, 1758) | Coleoptera | Coccinellidae | predatory | 1 | 4 | 1 | 2 |
| Coriomeris denticulatus (Scopoli, 1763) | Hemiptera | Coreidae | phytophagous | 1 | 1 | 0 | 0 |
| Dolycoris baccarum (Linnaeus, 1758) | Hemiptera | Pentatomidae | phytophagous | 2 | 3 | 2 | 2 |
| Eurydema oleracea (Linnaeus, 1758) | Hemiptera | Pentatomidae | phytophagous | 0 | 2 | 0 | 0 |
| Eurydema ornata (Linnaeus, 1758) | Hemiptera | Pentatomidae | phytophagous | 11 | 0 | 0 | 2 |
| Formica cunicularia Latreille, 1798 | Hymenoptera | Formicidae | omnivore | 0 | 3 | 0 | 0 |
| Isophya zubovskii Bey-Bienko, 1954 | Orthoptera | Tettigoniidae | phytophagous | 0 | 0 | 0 | 1 |
| Lixus (Eulixus) canescens Steven, 1829 | Coleoptera | Curculionidae | phytophagous | 0 | 0 | 2 | 0 |
| Melanobaris carbonaria (Boheman 1836) | Coleoptera | Curculionidae | phytophagous | 0 | 0 | 1 | 0 |
| Peribalus strictus subsp. vernalis (Wolff, 1804) | Hemiptera | Pentatomidae | phytophagous | 0 | 1 | 0 | 0 |
| Phymata crassipes (Fabricius, 1775) | Hemiptera | Reduviidae | predatory | 0 | 0 | 0 | 1 |
| Protaetia (Philhelena) ungarica (Herbst, 1790) | Coleoptera | Scarabaeidae | phytophagous | 3 | 0 | 0 | 0 |
| Psyllobora (Thea) vigintiduopunctata (Linnaeus, 1758) | Coleoptera | Coccinellidae | omnivore | 0 | 0 | 1 | 0 |
| Spermophagus calystegiae Lukjanovitch & Ter-Minassian, 1957 | Coleoptera | Chrysomelidae | phytophagous | 0 | 1 | 0 | 0 |
| Spermophagus sericeus (Geoffroy, 1785) | Coleoptera | Chrysomelidae | phytophagous | 1 | 4 | 1 | 0 |
| Teucriogethes distinctus (Sturm, 1845) | Coleoptera | Nitidulidae | phytophagous | 0 | 7 | 0 | 1 |
| Tropinota (Epicometis) hirta (Poda, 1761) | Coleoptera | Cetoniidae | phytophagous | 179 | 349 | 35 | 3 |
| Peleteria rubescens (Robineau-Desvoidy, 1830) | Diptera | Tachinidae | phytophagous | 1 | 0 | 1 | 0 |
| Metopoplax origani (Kolenati, 1845) | Hemiptera | Oxycarenidae | phytophagous | 0 | 0 | 1 | 0 |
| Valgus hemipterus (Linnaeus, 1758) | Coleoptera | Scarabaeidae | phytophagous | 0 | 0 | 0 | 1 |
| Cantharis sp. | Coleoptera | Cantharidae | omnivore | 0 | 1 | 1 | 0 |
| Lygaeus sp. | Hemiptera | Lygaeidae | phytophagous | 0 | 0 | 1 | 0 |
| Orius sp. | Hemiptera | Anthocoridae | predatory | 0 | 0 | 1 | 0 |
| Carpocoris sp. | Hemiptera | Pentatomidae | phytophagous | 0 | 1 | 0 | 0 |
| Ceutorhynchus sp. | Coleoptera | Curculionidae | phytophagous | 0 | 3 | 0 | 0 |
| Polistes sp. | Hymenoptera | Vespidae | omnivore | 0 | 0 | 1 | 0 |
Plant-insect relationships are key elements in the functioning of ecosystems, influencing both plant reproductive success and the structure of invertebrate communities (
Analyses conducted in four locations in the Moldova region showed that the structure of insect communities varied depending on the type of plant association, topographic characteristics (elevation, aspect, and slope), and functional traits of C. tataria. Inflorescence circumference and plant height showed significant positive correlations with the abundance of some species, such as Cercopis sanguinolenta, Eurydema ornata, or Bibio hortulanus, suggesting that these functional traits have probably a role in attracting certain trophic groups.
In this context, it has been shown in the literature that species such as Melanobaris carbonaria feed on vegetative parts of C. tataria (
Statistically significant relationships between plant height and inflorescence circumference and certain insect species, such as Bibio hortulanus and Cercopis sanguinolenta, suggest that morphological traits of C. tataria influence habitat selection and resource use by these species. This may reflect a specific ecological association or a preference for larger floral displays. In contrast, the lack of significant relationships for species, such as Camponotus piceus and Tropinota (Epicometis) hirta indicates that other ecological or behavioural factors likely drive their occurrence.
Beyond trait–insect relationships, the overall insect assemblage highlights the conservation value of habitats hosting C. tataria. Although most species were relatively common, two rare or vulnerable taxa (Lixus canescens and Clanoptilus affinis) were recorded, one of which was confirmed in the Romanian fauna after more than a century (
Most of the species are relatively common; however, a few are particularly noteworthy, especially in relation to the vegetative parts of C. tataria. Clanoptilus (Clanoptilus) affinis (Coleoptera: Malachiidae) is a small beetle species typically found in steppe habitats, classified as a Euro-Asiatic taxon. Like other members of the Malachiidae family, adults primarily feed on pollen (
Another noteworthy species associated with the vegetative parts of C. tataria is Protaetia (Philhelena) ungarica (Coleoptera: Cetoniidae). This beetle species is found across Central Europe and Asia, typically inhabiting steppe-like habitats (
Lixus (Eulixus) canescens (Coleoptera: Curculionidae) inhabits xerothermic, steppe or coastal habitats and it is distributed only in Romania, Moldova, Ukraine and the European part of Russia (
This is the first study to present an assessment of the insect community associated with C. tataria in Romania. The results showed that phytophagous species dominate insect communities, and the variation in functional traits is linked to the abundance of several insect species. Although insect diversity was moderate, two rare or vulnerable species were observed, highlighting the conservation value of the habitats where C. tataria occurs. Horlești and Miroslava differ the most from the other sites in insect species composition. The collected data show the importance of this steppe relict as a structural and trophic resource in dry grasslands. Further long-term studies are needed to clarify the pollination interactions, seasonal variation of insect communities, and the ecological mechanisms linking functional traits to insect visitation patterns.
The authors would like to thank some entomologists who kindly assisted with the identification of several insect specimens. The work of the second author A.M.P. was based on the infrastructure support from the Operational Program Competitiveness 2014–2020, Axis 1, under POC/448/1/1 Research infrastructure projects for public R&D institutions/Sections F 2018, through the Research Center with Integrated Techniques for Atmospheric Aerosol Investigation in Romania (RECENT AIR) project, under grant agreement MySMIS no. 127324.
Environmental and morphological characteristics of plots with Crambe tataria.
List of plant species from plots with Crambe tataria.
List of insect species collected on Crambe tataria inflorescences.
Relationship between inflorescence circumference of Crambe tataria and associated insect species. Statistical details are described in the Materials and Methods section (Kendall’s tau correlation).
Relationship between plant height of Crambe tataria and associated insect species. Statistical details are described in the Materials and Methods section (Kendall’s tau correlation).