[go: up one dir, main page]
More Web Proxy on the site http://driver.im/
You seem to have javascript disabled. Please note that many of the page functionalities won't work as expected without javascript enabled.
 
 
Sign in to use this feature.

Years

Between: -

Subjects

remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline

Journals

Article Types

Countries / Regions

Search Results (13)

Search Parameters:
Keywords = floral strips

Order results
Result details
Results per page
Select all
Export citation of selected articles as:
18 pages, 2892 KiB  
Article
Effects of Roasting Process on Sensory Qualities, Color, Physicochemical Components, and Identification of Key Aroma Compounds in Hubei Strip-Shaped Green Tea
by Fei Ye, Anhui Gui, Xiaoyan Qiao, Panpan Liu, Xueping Wang, Shengpeng Wang, Lin Feng, Jin Teng, Jinjin Xue, Xun Chen, Yuanhong Mei, Binghua Zhang, Hanshan Han, Anhua Liao, Pengcheng Zheng and Shiwei Gao
Metabolites 2025, 15(3), 155; https://doi.org/10.3390/metabo15030155 - 25 Feb 2025
Viewed by 142
Abstract
Background: Roasting conditions significantly influence the sensory profile of Hubei strip-shaped green tea (HSSGT). Methods: This study examined the effects of roast processing on the sensory attributes, color qualities, physicochemical properties, and key aroma compounds of HSSGT. Sensory evaluation, color qualities determination, principal [...] Read more.
Background: Roasting conditions significantly influence the sensory profile of Hubei strip-shaped green tea (HSSGT). Methods: This study examined the effects of roast processing on the sensory attributes, color qualities, physicochemical properties, and key aroma compounds of HSSGT. Sensory evaluation, color qualities determination, principal component analysis of physicochemical components (PCA), HS-SPME (headspace solid-phase microextraction) coupled with GC-MS (gas chromatography–mass spectrometry), relative odor activity value (ROAV), gas chromatography–olfactometry (GC-O), and absolute quantification analysis were employed to identify the critical difference in compounds that influence HSSGT desirability. Results: The results indicated that HSSGT roasted at 110 °C for 14 min achieved the highest sensory scores, superior physicochemical qualities, and an enhanced aroma index, which was attributed to shifting the proportion of chestnut to floral volatile compounds. Additionally, sensory-guided ROAV, GC-O, and absolute quantification revealed that linalool, octanal, nonanal, and hexanal were the most significant volatile compounds. The variations in these four critical compounds throughout the roasting process were further elucidated, showing that the ideal roasting conditions heightened floral aromas while diminishing the presence of less desirable green odors. These findings offer technical guidance and theoretical support for producing HSSGT with a more desirable balance of chestnut and floral aroma characteristics. Full article
Show Figures

Figure 1

Figure 1
<p>Hubei strip-shaped green tea (HSSGT) manufacturing process. (<b>A</b>) Flow chart of HSSGT processing and determination of optimal roasting temperature. (<b>B</b>) Flow chart outlining the determination of optimal roasting time and roasting parameter.</p>
Full article ">Figure 2
<p>Sensory quality scores of roasted HSSGT. (<b>A</b>) Sensory scores at different temperatures. (<b>B</b>) Sensory scores for varying roasting times at 110 °C.</p>
Full article ">Figure 3
<p>Color quality scores of HSSGT roasted at 110 °C for different durations. (<b>A</b>) Dry tea color analysis. (<b>B</b>) Brew color analysis. Each sample was performed in triplicate. Columns labeled with ‘a’, ‘b’, and ‘c’ had significant differences (<span class="html-italic">p</span> &lt; 0.05) from each other.</p>
Full article ">Figure 4
<p>Changes in bioactive compound content of HSSGT roasted at 110 °C for varying durations. (<b>A</b>) Tea polyphenol; (<b>B</b>) Free amino acids; (<b>C</b>) Soluble sugar; (<b>D</b>) Gallic acid; (<b>E</b>) Caffeine; (<b>F</b>) GC; (<b>G</b>) C; (<b>H</b>) EC; (<b>I</b>) EGC; (<b>J</b>) ECG; (<b>K</b>) EGCG; (<b>L</b>) GCG; (<b>M</b>) Ester catechins; (<b>N</b>) Total catechins. Columns labeled with ‘a’, ‘b’, and ‘c’ had significant differences (<span class="html-italic">p</span> &lt; 0.05) from each other.</p>
Full article ">Figure 5
<p>Characterization of HSSGT VOCs. (<b>A</b>) The abundance of specific categories of VOCs in HSSGT roasted for 6, 14, and 22 min. (<b>B</b>) Principal component analysis. (<b>C</b>) Heat map of main differential alcohol compounds. (<b>D</b>) Aroma index. Columns labeled with ‘a’, ‘b’, and ‘c’ had significant differences (<span class="html-italic">p</span> &lt; 0.05) from each other.</p>
Full article ">Figure 6
<p>Changes in the abundance of nonanal, linalool, hexanal, and octanal in the HSSGT roasting process. The different letters (‘a’, ‘b’, and ‘c’) indicate significant differences (<span class="html-italic">p</span> &lt; 0.05).</p>
Full article ">Figure 7
<p>Proposed pathways for molecular formation of the four characteristic HSSGT aroma compounds: (<b>A</b>) linalool, (<b>B</b>) nonanal, (<b>C</b>) octanal, (<b>D</b>) hexanal.</p>
Full article ">
18 pages, 4131 KiB  
Article
Influence of Floral Strip Width on Spider and Carabid Beetle Communities in Maize Fields
by Jia-Lu Li, Lan-Mei Huang, Zi-Yi Xiang, Jian-Ning Zhao, Dian-Lin Yang, Hui Wang and Yan-Jun Zhang
Insects 2024, 15(12), 993; https://doi.org/10.3390/insects15120993 - 15 Dec 2024
Viewed by 931
Abstract
The study explored the impact of floral strip width on the spider and carabid beetle communities in maize fields over two years. Three widths of floral strips (2 m, 4 m, and 6 m) were compared with maize-only control strips to evaluate species [...] Read more.
The study explored the impact of floral strip width on the spider and carabid beetle communities in maize fields over two years. Three widths of floral strips (2 m, 4 m, and 6 m) were compared with maize-only control strips to evaluate species diversity and distribution. The results showed significant differences in both spider and carabid populations between floral and control strips, with 4 m and 6 m widths consistently harboring higher biodiversity. The results also showed distinct community clustering within floral strips in 2021, which became more cohesive by 2022. Further analysis validated significant community dissimilarities between different strip widths and controls, highlighting the ecological advantages of wider floral strips for enhancing natural enemy biodiversity. Spider activity density was notably higher in floral strips than in adjacent farmland, peaking at the edges of 4 m-wide strips and decreasing in 6 m-wide strips, with the lowest density in 2 m-wide strips. Carabid beetle activity density varied considerably with strip width and proximity to the edge, typically peaking at the edges of wider strips. Spiders were more responsive to strip width than carabid beetles. Based on these findings, we suggest using 4 m- or 6 m-wide floral strips to enhance biodiversity and natural pest control in agricultural landscapes; the floral strips narrower than 4 m (such as 2 m) could not support optimal biodiversity, as spiders and carabid beetles do not disperse far into the maize field, with spiders having dispersal distances of less than 3 m and carabid beetles less than 10 m. Vegetation characteristics significantly influenced spider and carabid communities, impacting species richness, diversity indices, and community structures across two study years. These insights highlight the necessity of thoughtfully designing floral strips to enhance biodiversity and natural pest control in agricultural landscapes. Full article
(This article belongs to the Section Insect Ecology, Diversity and Conservation)
Show Figures

Figure 1

Figure 1
<p>(<b>A</b>) schematic representation showing the spatial arrangement of floral/control strips and their arthropod sampling sites within each replicate, (<b>B</b>) a photograph of 2 m-wide floral strip as example, and (<b>C</b>) a photograph of 2 m-wide maize planted control strip as example.</p>
Full article ">Figure 2
<p>Species richness, active density, and Shannon Diversity Index of spiders in floral strips and control strips. (<b>A</b>–<b>C</b>) in 2021 and (<b>D</b>–<b>F</b>) in 2022. 2m-T: 2m-wide floral strip, 2m-C: 2 m-wide control strip. 4m-T: 4 m-wide floral strip, 4m-C: 4 m-wide control strip. 6m-T: 6 m-wide floral strip, 6m-C: 6 m-wide control strip. Boxplots display the interquartile range (25–75%; box) and the median (line in the box). Whiskers represent 1.5 times the lower or upper interquartile range. Different lowercase letters above bars indicate significant differences among treatments.</p>
Full article ">Figure 3
<p>Species richness, active density, and Shannon Diversity Index of carabids in floral strips and control strips. (<b>A</b>–<b>C</b>) in 2021 and (<b>D</b>–<b>F</b>) in 2022. 2m-T: 2 m-wide floral strip, 2m-C: 2 m-wide control strip. 4m-T: 4 m-wide floral strip, 4m-C: 4 m-wide control strip. 6m-T: 6 m-wide floral strip, 6m-C: 6 m-wide control strip. Boxplots display the interquartile range (25–75%; box) and the median (line in the box). Whiskers represent 1.5 times the lower or upper interquartile range. Different lowercase letters above bars indicate significant differences among treatments.</p>
Full article ">Figure 4
<p>Non-linear multi-dimensional scaling (NMDS) based on chord measure of spiders and carabids communities in floral strips and control strips. (<b>A</b>) Spiders in 2021, (<b>B</b>) carabids in 2021, (<b>C</b>) spiders in 2022, and (<b>D</b>) carabids in 2022.</p>
Full article ">Figure 5
<p>Active density of (<b>A</b>) Spiders and (<b>B</b>) carabids within floral strip (−1 m), at strip edge (0 m), and in adjacent farmland (1 m). 2m-T: 2 m-wide floral strip, 4m-T: 4 m-wide floral strip, 6m-T: 6 m-wide floral strip. Data presented as mean ± SE. Different lowercase and uppercase letters above bars indicated significant differences among distances for each width of floral strip and widths for each distance from edge, respectively.</p>
Full article ">Figure 6
<p>Active density of spiders and carabids at various distances from the strip edge into adjacent maize fields. (<b>A</b>) Spiders in 2021, (<b>B</b>) carabids in 2021, (<b>C</b>) spiders in 2022, and (<b>D</b>) carabids in 2022. 2m-T: 2 m-wide floral strip, 4m-T: 4 m-wide floral strip, 6m-T: 6 m-wide floral strip. Data presented as mean ± SE. Different lowercase in the tables denoted significant differences among distances for each width of floral strip.</p>
Full article ">Figure 7
<p>Redundance analysis (RDA) of spiders and carabids assemblage structures and vegetation characteristics of floral strips. (<b>A</b>) Spiders in 2021, (<b>B</b>) carabids in 2021, (<b>C</b>) spiders in 2022, and (<b>D</b>) carabids in 2022.</p>
Full article ">
22 pages, 2708 KiB  
Article
Biodiverse Management of Perennial Flower Margins in Farmland: Meandering Mowing by ‘Three-Strip Management’ to Boost Pollinators and Beneficial Insects
by Laurian Parmentier, Hannah Vanderstappen and Geert Haesaert
Insects 2024, 15(12), 953; https://doi.org/10.3390/insects15120953 - 30 Nov 2024
Viewed by 1520
Abstract
Agricultural intensification has led to significant declines in beneficial insect populations, such as pollinators and natural enemies, along with their ecosystem services. The installation of perennial flower margins in farmland is a popular agri-environmental scheme to mitigate these losses, promoting biodiversity, pollination, and [...] Read more.
Agricultural intensification has led to significant declines in beneficial insect populations, such as pollinators and natural enemies, along with their ecosystem services. The installation of perennial flower margins in farmland is a popular agri-environmental scheme to mitigate these losses, promoting biodiversity, pollination, and pest control. However, outcomes can vary widely, and recent insights into flower margins in an agricultural context suggest that management could be an important contributor to this variation. This study evaluated two mowing management regimes: the new “three-strip management” method with uneven, curved mowing lines and regular phased mowing as a control method. During the third year of application, we evaluated the effects on the alpha diversity indices of pollinators and natural enemies, as well as plant–pollinator visitation networks. Curved three-strip management significantly increased the abundance of all pollinator groups (+44%) and natural enemies (+50%), and the taxonomic richness and diversity of pollinators, especially for rarer solitary bees. Floral diversity was also higher, with more unique plants blooming in early spring and late summer, generating more unique plant–pollinator interactions (+54%) and a positive impact on multiple network-level properties. Our findings provide new evidence that nature-based management methods can be a win–win solution, creating high-quality habitats that enhance the insect diversity of various groups, support associated ecosystem services, and help restore overall farmland biodiversity. Full article
(This article belongs to the Special Issue Pollinator Biodiversity and Ecosystem Services)
Show Figures

Graphical abstract

Graphical abstract
Full article ">Figure 1
<p>Selected locations in Flanders (Belgium) and paired sites (indicated with a unique color) of perennial flower margins (in the center, indicated in red) with either three-strip or regular management, and surrounding land cover (within a radius of 500 m) mapped for each study site.</p>
Full article ">Figure 2
<p>Illustrating the combined effect of three successive mowing cycles on a margin when regular versus three-strip management is applied, according to Parmentier (2023) [<a href="#B36-insects-15-00953" class="html-bibr">36</a>]. (<b>a</b>). The first mowing line, starting from an unmown margin. The margin is longitudinally divided into three equal strips, of which one-third will be kept unmown (ratio of mown/unmown is set at 2:1). When applying three-strip management, a curved instead of a straight mowing line is used. (<b>b</b>). The result after the first mowing cycle in the first season (uniform green zones are mown), normally applied at the end of June, and an illustration of the second mowing line. (<b>c</b>). The result after the second mowing cycle, normally applied at the end of September in the same season, and an illustration of the third mowing line. (<b>d</b>). Result after the third mowing cycle, the first of the second season. (<b>e</b>). Overlay illustrating the effect after three mowing cycles when either regular or three-strip management is applied, respectively (unequally mown zones in different grey tones; unmown zones in green).</p>
Full article ">Figure 3
<p>Plant species coverage for regular versus three-strip management. Blue elements represent individual plant species coverage (%) based on full study site estimations (Tansley scale), averaged per period and management method. Blue color intensity represents the coverage percentage. Black framed elements highlight unique blooming plant species observed per management type during each period (P1–P4).</p>
Full article ">Figure 4
<p>Plant–pollinator visitation networks. Visualization based on all bees observed on flowers during the third year of successive mowing, when applying regular rotational management (<b>a</b>). versus three-strip management (<b>b</b>). The most frequent flower–pollinator interactions and visits are highlighted in pale orange. The total number of plant–bee interactions was significantly higher within three-strip-managed sites; other networks and network properties are listed in <a href="#insects-15-00953-t002" class="html-table">Table 2</a>.</p>
Full article ">
15 pages, 2537 KiB  
Article
Dynamic Changes in Aroma Compounds during Processing of Flat Black Tea: Combined GC-MS with Proteomic Analysis
by Cun Ao, Xiaojun Niu, Daliang Shi, Xuxia Zheng, Jizhong Yu and Yingbin Zhang
Foods 2024, 13(20), 3243; https://doi.org/10.3390/foods13203243 - 12 Oct 2024
Viewed by 1321
Abstract
Flat black tea (FBT) has been innovatively developed to alleviate homogenisation competition, but the dynamic changes in aroma components during the process remain unclear. This study employed HS-SPME-GC-MS to analyse the aroma components of tea samples from various processing stages of FBT, and [...] Read more.
Flat black tea (FBT) has been innovatively developed to alleviate homogenisation competition, but the dynamic changes in aroma components during the process remain unclear. This study employed HS-SPME-GC-MS to analyse the aroma components of tea samples from various processing stages of FBT, and to make a comparative assessment with conventional strip-like Congou black tea (SBT). Additionally, a proteomic analysis was conducted on fresh leaves, withered leaves, and frozen–thawed leaves. Significant changes were observed in the aroma components and proteins during the processing. The results of the multivariate and odour activity value analysis demonstrated that the principal aroma components present during the processing of FBT were linalool, (E)-2-hexen-1-al, methyl salicylate, geraniol, hexanal, benzeneacetaldehyde, (Z)-3-hexenyl butyrate, dimethyl sulphide, 2-methylbutanal, 2-ethylfuran, nonanal, nonanol, 3-methylbutanal, (Z)-3-hexen-1-ol, 2-pentylfuran, linalool oxide I, and β-myrcene. Freezing–thawing and final roasting are the key processing steps for forming the aroma quality of FBT. The final roasting yielded a considerable quantity of pyrazines and pyrroles, resulting in a high-fried aroma, but caused a significant reduction in linalool, geraniol, β-myrcene, and esters, which led to a loss of floral and fruity aromas. The freezing–thawing treatment resulted in an accelerated loss of aroma substances, accompanied by a decrease in the expression level of lipoxygenase and 2-C-methyl-D-erythritol 2,4-cyclodiphosphate synthase. The formation of aroma substances in the linoleic acid metabolic pathway and terpenoid metabolic process was hindered, which had a negative impact on tea aroma. This study elucidates the causes of unsatisfactory aroma quality in tea products made from frozen tea leaves, providing theoretical support for the utilisation of frostbitten tea leaves, and helps us to understand the mechanism of aroma formation in black tea. Full article
Show Figures

Figure 1

Figure 1
<p>Processing flowchart of black tea.</p>
Full article ">Figure 2
<p>The sensory qualities of black tea. (<b>A</b>) Dried tea samples; (<b>B</b>) tea infusions; (<b>C</b>) the aroma profiles of the tea infusions. (*: <span class="html-italic">p</span> &lt; 0.05).</p>
Full article ">Figure 3
<p>Screening of differential aroma compounds. (<b>A</b>) PCA chart of all the samples during the black tea processing; (<b>B</b>) scores of OPLS-DA (R2Y = 0.999, Q2 = 0.990); (<b>C</b>) cross-validation by 200-times permutation test (R2 = 0.599, Q2 = −0.536); (<b>D</b>) heatmap visualisation constructed with the key differential components (VIP &gt; 1.0, OAV &gt; 1.0, and <span class="html-italic">p</span> &lt; 0.05).</p>
Full article ">Figure 4
<p>The proportion of different types of aroma substances during processing. (<b>A</b>) The manufacturing process of SBT; (<b>B</b>) the manufacturing process of FBT.</p>
Full article ">Figure 5
<p>Key aroma components in FBT manufacturing process. (<b>A</b>) Scores of OPLS-DA (R2Y = 0.968, Q2 = 0.900); (<b>B</b>) cross-validation by 200-times permutation test (R2 = 0.303, Q2 = −0.994); (<b>C</b>) aroma components of variables important in projecting (VIP &gt; 1).</p>
Full article ">Figure 6
<p>The number of proteins identified in the study. (<b>A</b>) The number of proteins identified in different sample; (<b>B</b>) PCA chat; (<b>C</b>) differential proteins as a volcano plot of FWL vs. FL; (<b>D</b>) differential proteins as a volcano plot of FTL vs. FWL.</p>
Full article ">Figure 7
<p>Metabolic pathway of key aroma compounds. (<b>A</b>) The synthesis pathway of terpenes; (<b>B</b>) the metabolic pathway of fatty acid-derived aroma compounds. The boxes of different colours from left to right are FL, FWL, FTL, FCL, FFL, FSL, and FBT; red and green colours represent above-mean level and below-mean level, respectively. G3P: D-glyceradehyde-3-phosphate; Geranyl-PP: geranyl diphosphate; LOX: lipoxygenase.</p>
Full article ">
12 pages, 1253 KiB  
Article
Enhancing Coccinella Beetle Biological Pest Control via a Floral Approach in Cucumber Greenhouse
by Moazam Hyder, Yuyan Li, Muhammad Fahad Raza, Maosen Zhang, Junjie Chen, Jianjun Mao, Aslam Bukero and Lisheng Zhang
Life 2023, 13(10), 2080; https://doi.org/10.3390/life13102080 - 19 Oct 2023
Cited by 1 | Viewed by 1845
Abstract
Flower-rich habitats are crucial for promoting biodiversity and ecosystem services within agricultural ecosystems, such as pollination and pest control. The present study investigates the efficacy of employing floral structures as a criterion for the selection of plant species in order to enhance the [...] Read more.
Flower-rich habitats are crucial for promoting biodiversity and ecosystem services within agricultural ecosystems, such as pollination and pest control. The present study investigates the efficacy of employing floral structures as a criterion for the selection of plant species in order to enhance the attraction of natural enemies within cucumber greenhouses, consequently augmenting floral resources. The results of our study provide evidence that flower strips have a beneficial effect on the fitness of critical natural predators, while not facilitating the proliferation of detrimental insect species. These findings exhibit potential for enhancing pest-management services in the agricultural sector. The findings of our study demonstrate that pest levels within greenhouse environments closely resemble those observed in real-world commercial cropping systems. As a result, the introduction of Coccinella septempunctata and Menochilus sexmaculatus biocontrol agents is confirmed to be a reliable and efficient method for pest management. The phenomenon of predator–prey density dependency is recognized as a crucial element in the implementation of biological control strategies. Furthermore, we investigate the impact of floral resources on the reproductive capacity of indigenous predators. The impact of Coriandrum sativum on fertility is substantial, indicating that the presence of a varied plant assortment with overlapping flowering periods can prolong the availability of floral resources. This study highlights the significance of flower-rich habitats and deliberate plant selection in augmenting biodiversity, ecosystem services, and pest management within agricultural settings. The implementation of conservation biological control technologies presents supplementary ecological advantages, thus offering practical implications for the promotion of sustainable agricultural practices. Full article
Show Figures

Figure 1

Figure 1
<p>The average number (±SE) per plant of aphids in a cucumber greenhouse at different time intervals: The green bar represents MScR, light brown represents MS, black shows CScR, yellow indicates CS, and blue represents control. The mean population of <span class="html-italic">Myzus persicae</span> in cucumber greenhouses with the presence of natural enemies and floral plants (<span class="html-italic">Coriandrum sativum</span>) and natural enemies without floral plants MScR = <span class="html-italic">M. sexmaculatus</span> + <span class="html-italic">C. sativum</span>; MS = <span class="html-italic">M. sexmaculatus</span>; CScR = <span class="html-italic">C. septempunctata</span> + <span class="html-italic">C. sativum</span>; CS = <span class="html-italic">C. septempunctata</span> at different D = days and W = weeks of observation. Different letters indicate statistically significant differences between treatments. ANOVAs with Tukey HSD post hoc tests were used to compare treatments.</p>
Full article ">Figure 2
<p>Population reduction in aphids in cucumber greenhouses at different time intervals: the aphid population decreased significantly with the passage of time. The black bar represents MScR, red represents MS, the light blue colour shows CScR, and the green colour represents the reduction in <span class="html-italic">Myzus persicae</span> in cucumber greenhouses with the presence of natural enemies and floral plants (<span class="html-italic">Coriandrum sativum</span>) and natural enemies without floral plants MScR = <span class="html-italic">M. sexmaculatus</span> + <span class="html-italic">C. sativum</span>; MS = <span class="html-italic">M. sexmaculatus</span>; CScR = <span class="html-italic">C. septempunctata</span> + <span class="html-italic">C. sativum</span>; CS = <span class="html-italic">C. septempunctata</span> at different D = days and W = weeks of observation. The reduction percentage in aphid and whitefly was determined using Abbott’s formula. Different letters indicate statistically significant differences between treatments. ANOVAs with Tukey HSD post hoc tests were used to compare treatments.</p>
Full article ">Figure 3
<p>The average number (±SE) per plant of whitefly in a cucumber greenhouse at different time intervals: The green bar represents MScR, light brown represents MS, black shows CScR, yellow indicates CS, and blue represents control. The mean population of <span class="html-italic">Bamisia tabaci</span> in cucumber greenhouses with the presence of natural enemies and floral plants (<span class="html-italic">Coriandrum sativum</span>) and natural enemies without floral plants MScR = <span class="html-italic">M. sexmaculatus</span> + <span class="html-italic">C. sativum</span>; MS = <span class="html-italic">M. sexmaculatus</span>; CScR = <span class="html-italic">C. septempunctata</span> + <span class="html-italic">C. sativum</span>; CS = <span class="html-italic">C. septempunctata</span> at different D = days and W = weeks of observation. Different letters indicate statistically significant differences between treatments. ANOVAs with Tukey HSD post hoc tests were used to compare treatments.</p>
Full article ">Figure 4
<p>Population reduction in whiteflies in cucumber greenhouses at different time intervals: the aphid population decreased significantly with the passage of time. The black bar represents MScR, red represents MS, the light blue colour shows CScR, and the green colour represents CS. The reduction in <span class="html-italic">Bemisia tabaci</span> in the cucumber greenhouse with the presence of natural enemies and floral plants (<span class="html-italic">Coriandrum sativum</span>) and natural enemies without floral plants MScR = <span class="html-italic">M. sexmaculatus</span> + <span class="html-italic">C. sativum</span>; MS = <span class="html-italic">M. sexmaculatus</span>; CScR = <span class="html-italic">C. septempunctata</span> + <span class="html-italic">C. sativum</span>; CS = <span class="html-italic">C. septempunctata</span> at different D = days and W = weeks of observation. The reduction percentage in aphid and whitefly was determined using Abbott’s formula. Different letters indicate statistically significant differences between treatments. ANOVAs with Tukey HSD post hoc tests were used to compare treatments.</p>
Full article ">Figure 5
<p>The fecundity rate of <span class="html-italic">M. sexmaculatus</span> and <span class="html-italic">C. septempunctata</span> in a cucumber greenhouse with the presence of a floral plant (<span class="html-italic">Coriandrum sativum</span>) and natural enemies without floral plants MScR = <span class="html-italic">M. sexmaculatus</span> + <span class="html-italic">C. sativum</span>, MS = <span class="html-italic">M. sexmaculatus</span>; CScR = <span class="html-italic">C. septempunctata</span> + <span class="html-italic">C. sativum</span>; CS = <span class="html-italic">C. septempunctata</span> at different times and W = weeks of observation. Shows the average eggs laid per plant. There was a significant effect between treatments; MS plots had significantly fewer eggs than MScR plots over time and a similar trend was observed between CS and CScR plots. ANOVAs with Tukey HSD post hoc tests were used to compare treatments. The different letters indicate statistically significant differences between treatments.</p>
Full article ">
9 pages, 1305 KiB  
Article
Response of Superoxide Dismutase (SOD) to Homogeneous and Heterogeneous Food Sources in Bumblebees (Bombus terrestris) and Honeybees (Apis mellifera)
by María José Ludewig, Klaus-Peter Götz, Claudia S. Romero-Oliva, Patricia Landaverde and Frank-M. Chmielewski
Physiologia 2023, 3(2), 272-280; https://doi.org/10.3390/physiologia3020019 - 27 Apr 2023
Cited by 1 | Viewed by 2323
Abstract
The conception of “floral strips” is a strategy to provide more and different food sources for pollinators. The impact of “homogeneous” Phacelia tanacetifolia (“Phacelia”) and “heterogeneous” (flower mix) food sources on the enzyme activity of bumblebees (Bombus terrestris) and honeybees ( [...] Read more.
The conception of “floral strips” is a strategy to provide more and different food sources for pollinators. The impact of “homogeneous” Phacelia tanacetifolia (“Phacelia”) and “heterogeneous” (flower mix) food sources on the enzyme activity of bumblebees (Bombus terrestris) and honeybees (Apis mellifera) under urban conditions has not been reported. Organisms responding to challenging environmental conditions are known to exhibit increases in oxidative stress parameters which in turn affect both physiological and metabolic parameters. A field study was conducted in Berlin-Dahlem, Germany, using the response of the “marker” enzyme superoxide dismutase (SOD) on food sources for assessment. SOD data is also shown from the wild bee Megachile rotundata (Fabricius 1787), obtained from three different locations in the federal state Brandenburg, Germany. The results demonstrate that the enzyme activity of SOD significantly increased in bumblebees visiting the flower mix compared to the Phacelia. The experimental approach had individual effects at the level of the species, bumblebees and honeybees, respectively. The activity of the biomarker SOD could be successfully used to assess the effects of the compositions of homogeneous and heterogeneous flower fields. Full article
Show Figures

Figure 1

Figure 1
<p>Example of the construction and installation of the trap nests in the federal state of Brandenburg, Germany.</p>
Full article ">Figure 2
<p>Schematic depiction of Phacelia plot at Free University Berlin (FU) and the flower mix plot at Albrecht Daniel Thaer-Institute (ADTI, HU) (<uri>https://www.google.de/intl/de/earth/index.html</uri>, accessed on 6 March 2023).</p>
Full article ">Figure 3
<p>Schematic flow diagram for processing <italic>Bombus terrestris</italic> and <italic>Apis mellifera</italic> before superoxide dismutase (SOD) measurement by LABOKLIN.</p>
Full article ">
14 pages, 641 KiB  
Article
You Reap What You Sow: A Botanical and Economic Assessment of Wildflower Seed Mixes Available in Ireland
by Claudia Barry and Simon Hodge
Conservation 2023, 3(1), 73-86; https://doi.org/10.3390/conservation3010007 - 24 Jan 2023
Cited by 4 | Viewed by 3664
Abstract
Planting wildflower seed mixes has become popular with individuals and community groups aiming to promote wildlife and enhance local biodiversity. Recently, however, these seed mixes have been criticized with respect to the origin of the seeds and the species they contain. There is [...] Read more.
Planting wildflower seed mixes has become popular with individuals and community groups aiming to promote wildlife and enhance local biodiversity. Recently, however, these seed mixes have been criticized with respect to the origin of the seeds and the species they contain. There is a growing awareness that the unintended planting of exotic species may disrupt native ecological networks, introduce aggressive weeds, or facilitate the establishment of invasive species in new localities. In this study, we purchased two packets of twelve brands of wildflower seeds available in Ireland from stores or online suppliers. In total, the 24 packets contained 69,409 seeds weighing 304 g, and represented 92 plant species in 23 families. Only 25% of the seed packets purchased in Ireland originated from Ireland, and only 43% of the plant species we identified are considered native to Ireland. To reinforce this point, the most frequent species, Phacelia tanacetifolia, which occurred in nine of the twelve brands, is not a native Irish plant species. Multivariate analysis identified no obvious grouping of seed mixes based on their intended target group (e.g., bees, butterflies, wildlife), which might be expected had manufacturers followed scientific guidance describing which plants are preferred by which pollinator group. The creation of patches of diverse floral habitats in gardens and urban settings can significantly benefit wildlife and human wellbeing. Our results, however, reinforce the need for caution before using wildflower mixes in attempts to restore or recreate natural or semi-natural plant communities. Full article
Show Figures

Figure 1

Figure 1
<p>NMDS plots comparing composition of wildflower seed mixes based on presence or absence of each species, the seed count, the seed weight, and potential composition of final flowering mix based on germination rate of each species in each brand. BEE—bee-targeted brands; BUT—butterfly-targeted brands; WDL—wildlife targeted brands; WFL—wildflower mixes with no obvious target species/group on packaging.</p>
Full article ">
10 pages, 3306 KiB  
Article
Accurate and Rapid Genetic Tracing the Authenticity of Floral Originated Honey with the Molecular Lateral Flow Strip
by Qian Wu, Qi Chen, Chao Yan, Jianguo Xu, Zhaoran Chen, Li Yao, Jianfeng Lu, Bangben Yao and Wei Chen
Biosensors 2022, 12(11), 971; https://doi.org/10.3390/bios12110971 - 4 Nov 2022
Cited by 1 | Viewed by 1787
Abstract
Honey is a natural product and is heavily consumed for its well-known nutritional functions. Honeys with different floral origins possess distinctive flavors, tastes, functions and economic values. It is vital to establish an effective strategy for identifying the authenticity of honey. The intrinsic [...] Read more.
Honey is a natural product and is heavily consumed for its well-known nutritional functions. Honeys with different floral origins possess distinctive flavors, tastes, functions and economic values. It is vital to establish an effective strategy for identifying the authenticity of honey. The intrinsic genetic materials of pollen were adopted as target analytes for the effective identification of honey with floral origins. With an optimized protocol for the rapid gene extraction from honey, target genetic templates were amplified on-site with a portable device. Conveniently, all on-site amplified functional products were easily judged by the designed lateral flow strip (LFS), which was defined as the molecular LFS in this research. Additionally, the entire on-site genetic authentication of honey was completed in less than 2 h by visual observation. Commercial honey products have been successfully identified with excellent accuracy. This low-cost, high-efficiency and easy-operational strategy will greatly benefit the quality guarantee of foods with specific functions and geographical markers. Full article
(This article belongs to the Special Issue Application of Biosensors in Food Safety Analysis)
Show Figures

Figure 1

Figure 1
<p>The schematic diagram of the rapid genetic authentication strategy for honey. The target DNA is first extracted by ultrasonication and amplified to produce the enormous functional amplicons with the designed primer set. The products of on-site amplifications were skillfully integrated with the molecular LFS and the detection results of amplicons can be easily and visually judged.</p>
Full article ">Figure 2
<p>The optimization results of ultrasonic time for pretreatment of honey samples: (<b>A</b>) The traditional metal bath method compared with the ultrasonication method for honey genome DNA extraction.; (<b>B</b>) Shows the DNA extraction efficiency after different ultrasonication time (0 min, 2 min, 5 min, 7 min, 10 min, and 15 min).</p>
Full article ">Figure 3
<p>Optimization of experimental parameters: (<b>A</b>) Primer concentration (0.04 μM, 0.08 μM, 0.12 μM, 0.16 μM and 0.35 μM); (<b>B</b>) Annealing temperature (50 °C, 53 °C, 55 °C, 58 °C and 61 °C); (<b>C</b>) Volume of antibody for conjugation (1 μL, 2 μL, 3 μL, 4 μL and 5 μL 1 mg/mL antibody); (<b>D</b>) Volume of K<sub>2</sub>CO<sub>3</sub> for pH adjustment (5 μL, 10 μL, 15 μL, 20 μL and 30 μL 0.1M K<sub>2</sub>CO<sub>3</sub>); (<b>E</b>) Suspension species (0.5%OVA, 10% BSA, 10% HSA, 0.5% Casein and 0.5% Casein−Na); (<b>F</b>) Categories of loading buffer (10 mM PBS, 10 mM Tris−HCL, 10 mM PB, 10 mM PBT and 10 mM Ac−AcNa).</p>
Full article ">Figure 4
<p>Authentication performance of the amplification−assisted molecular LFS: (<b>A</b>) Visual judgment results of honey samples adulterated at different ratio (0%, 10%, 25%, 50%, 75%, 90% and 100%, <span class="html-italic">v</span>/<span class="html-italic">v</span>%) and the corresponding quantitative curves analyzed by ImageJ; (<b>B</b>) Calibration curve of the authentication performance.</p>
Full article ">Figure 5
<p>Selectivity assay results of the amplification-assisted molecular LFS: (<b>A</b>) Visual observation results of amplification-assisted molecular LFS and corresponding curves of ImageJ treated results; (<b>B</b>) Quantitative analysis results of ImageJ treated results.</p>
Full article ">Figure 6
<p>Determination results of 14 commercial honey samples: (<b>A</b>) Visual analysis results and corresponding quantitative curves treated by ImageJ; (<b>B</b>) Quantitative analysis results by ImageJ.</p>
Full article ">
15 pages, 1440 KiB  
Article
Species-Enriched Grass-Clover Mixtures Can Promote Bumblebee Abundance Compared with Intensively Managed Conventional Pastures
by Henriette Beye, Friedhelm Taube, Katharina Lange, Mario Hasler, Christof Kluß, Ralf Loges and Tim Diekötter
Agronomy 2022, 12(5), 1080; https://doi.org/10.3390/agronomy12051080 - 29 Apr 2022
Cited by 11 | Viewed by 4530
Abstract
(1) Land use intensification has led to serious declines in biodiversity, including in forage production systems for dairy cows. Agri-environmental schemes, such as enriching grasslands in floral species, were shown to be an effective tool to promote biodiversity in higher trophic levels. Here, [...] Read more.
(1) Land use intensification has led to serious declines in biodiversity, including in forage production systems for dairy cows. Agri-environmental schemes, such as enriching grasslands in floral species, were shown to be an effective tool to promote biodiversity in higher trophic levels. Here, we studied an innovative pasture-based dairy production system with floral-species-enhanced temporary grasslands, with respect to the effect on wild bee abundance and species richness. (2) We studied three grass-clover mixtures with perennial ryegrass and clover species with different levels of plant diversity for flower cover and wild bees. The grass-clover pastures were rotationally stocked with cattle and parts of the pastures were excluded from grazing. Intensively managed conventional permanent grasslands were studied as the common land use type. Wild bees were caught by sweep netting. Wild bee diversity was analysed with a general linear mixed model. For species richness, an incidence-based coverage estimator was calculated. (3) In total, 541 wild bees from 10 species were found. No wild bees were caught on the conventional grasslands. Wild bee abundance and species richness did not differ among the three grass-clover mixtures, but with increasing flower cover of white clover (Trifolium repens), wild bee abundance increased. Except for one solitary wild bee individual, the recorded community exclusively consisted of bumblebees. While generalist species that are commonly found on farmland dominated, rare long-tongued bumblebees made up 10% on the grazed sites of the multispecies mixture and made up 20% on the ungrazed strips of the binary mixture and multispecies mixture. (4) We conclude that multispecies mixtures can provide resources for generalist bumblebee species, especially when compared with conventional grasslands that offer no resources. Considering that the multispecies mixture has been also shown to reduce greenhouse gas emissions and nitrate leaching, while maintaining high forage yields, our findings add to the potential to promote a wide range of ecosystem services. Yet, should their full potential be enfolded, grazing should partially be excluded, and the mixture should be extended by plant species with more open flowers, suitable for solitary wild bees. Full article
(This article belongs to the Section Grassland and Pasture Science)
Show Figures

Figure 1

Figure 1
<p>Effect of white clover flower cover on wild bee abundance on the mixtures and managements.</p>
Full article ">Figure 2
<p>Effect of white clover flower cover on ICE diversity index of wild bees on the different mixtures and managements.</p>
Full article ">Figure 3
<p>Numbers of wild bee individuals on grazed pastures and ungrazed strips (management) of the binary mixture and multispecies mixture.</p>
Full article ">
21 pages, 2408 KiB  
Article
The Role of Annual Flowering Plant Strips on a Melon Crop in Central Spain. Influence on Pollinators and Crop
by Celeste Azpiazu, Pilar Medina, Ángeles Adán, Ismael Sánchez-Ramos, Pedro del Estal, Alberto Fereres and Elisa Viñuela
Insects 2020, 11(1), 66; https://doi.org/10.3390/insects11010066 - 20 Jan 2020
Cited by 21 | Viewed by 5221
Abstract
Planting flower strips adjacent to crops is among the habitat-management practices employed to offer alternative floral resources to pollinators. However, more information is needed to understand their potential spill-over of pollinators on nearby insect-pollinated crops. Over the course of two consecutive years, the [...] Read more.
Planting flower strips adjacent to crops is among the habitat-management practices employed to offer alternative floral resources to pollinators. However, more information is needed to understand their potential spill-over of pollinators on nearby insect-pollinated crops. Over the course of two consecutive years, the suitability of a flower mixture of 10 herbaceous plants for pollinators was evaluated on a weekly basis, in a randomized block design of two melon plots (10 × 10 m2) with or without 1 m-wide flower strips. Floral coverage and pollinator visits to the plant species, as well as pollinator visits and the yield and quality of the crop, were assessed. Additionally, the selected mixture was tested for 1 year in a commercial field in order to ascertain how far the flower strip could influence visitors in the crop. The most suitable species for a flower strip in central Spain based on their attractiveness, floral coverage and staggered blossom were Coriandrum sativum L., Diplotaxis virgata L., Borago officinalis L. and Calendula officinalis L. The flower strip can act as either pollinator competitor or facilitator to the crop, depending on their floral coverage and/or the predominant species during the crop bloom period. The concurrence of blooming of the rewarding plant C. officinalis with the melon crop should be avoided in our area. In the commercial field, the bee visitation rate in the melon flowers decreased with the distance to the flower strip. No influence of the specific flower strip evaluated on crop productivity or quality was found. Full article
Show Figures

Figure 1

Figure 1
<p>Experimental design and location of La Poveda experimental plots (Madrid; Central Spain) and commercial melon field at Corral de Almaguer (Toledo; Central Spain) with the sampling area (2.8 ha, continuous line).</p>
Full article ">Figure 2
<p>Floral coverage in the flower strips of La Poveda experimental plots (Madrid) during the three bloom periods and of the commercial melon field at Corral de Almaguer (Toledo) and meteorological conditions (temperature and precipitation [<a href="#B53-insects-11-00066" class="html-bibr">53</a>]), The plants in bold were used in the statistical analyses of comparison between visitor groups and plant species each year.</p>
Full article ">Figure 3
<p>Visits (mean ± standard error (SE)) of beetles, hoverflies, small (&lt;1cm) short-tongued (S-T), large S-T and long-tongued (L-T) bees to different plants of a flower strip in La Poveda experimental plots, in different years and bloom periods. Means are observations of three blocks (six marked areas (1 × 1 m<sup>2</sup>)/plot, 3 min/marked area, 18 min in total) and those followed by the same letter are not significantly different within bloom periods and years. Linear mixed-effects model; Fisher’s least significant difference (LSD) post hoc; <span class="html-italic">p</span> &lt; 0.05. Number of flowers of each plant species was included as covariate. The pie-charts show the percentage of the different visitor groups or plant species within bloom periods and years.</p>
Full article ">Figure 4
<p>Visits (mean ± SE) to melon flowers in control plots or plots with flower strip of La Poveda experimental farm. * Indicates significant differences between treatments. NS = non-significant difference. Bee groups: small (&lt;1 cm) short-tongued (S-T); large S-T and long-tongued (L-T) bees. Means are observations of three blocks (three transects/plot, 3 min/transect, 9 min in total) and those followed by the same letter are not significantly different within years. Linear mixed-effects model, Fisher’s LSD post hoc, <span class="html-italic">p</span> &lt; 0.05.</p>
Full article ">Figure 5
<p>Bee visitation rate (mean visits·flower<sup>−1</sup> ± SE) in the flower strip and at different distances of the melon crop in the commercial field of Corral de Almaguer (Central Spain). Means are observations per flower and transect 15 m in length during 3 min, and those followed by the same letter within each distance are not significantly different. Generalized linear mixed model; Tukey post hoc tests; <span class="html-italic">p</span> &lt; 0.05.</p>
Full article ">
24 pages, 1186 KiB  
Review
Managing Floral Resources in Apple Orchards for Pest Control: Ideas, Experiences and Future Directions
by Annette Herz, Fabian Cahenzli, Servane Penvern, Lukas Pfiffner, Marco Tasin and Lene Sigsgaard
Insects 2019, 10(8), 247; https://doi.org/10.3390/insects10080247 - 11 Aug 2019
Cited by 54 | Viewed by 8155
Abstract
Functional biodiversity is of fundamental importance for pest control. Many natural enemies rely on floral resources to complete their life cycle. Farmers need to ensure the availability of suitable and sufficient floral biodiversity. This review summarizes 66 studies on the management of floral [...] Read more.
Functional biodiversity is of fundamental importance for pest control. Many natural enemies rely on floral resources to complete their life cycle. Farmers need to ensure the availability of suitable and sufficient floral biodiversity. This review summarizes 66 studies on the management of floral biodiversity in apple orchards, published since 1986. Approaches followed different degrees of intervention: short-term practices (mowing regime and weed maintenance, cover crops), establishment of durable ecological infrastructures (perennial flower strips, hedgerows) and re-design of the crop system (intercropping, agroforestry). Although short-term practices did not always target the nutrition of natural enemies by flowering plants, living conditions for them (alternative prey, provision of habitat) were often improved. Perennial flower strips reliably enhanced natural enemies and techniques for their introduction continuously developed. Resident natural enemies and their impact in pest control reacted positively to the introduction of a more diversified vegetation, whereas the response of very mobile organisms was often not directly linked to the measures taken. A careful selection and management of plants with particular traits exploitable by most natural enemies emerged as a key-point for success. Now the elaborated design of such measures needs to be adopted by stakeholders and policy makers to encourage farmers to implement these measures in their orchards. Full article
(This article belongs to the Special Issue Pest Control in Fruit Trees)
Show Figures

Figure 1

Figure 1
<p>Number of trials reported in publications considered in the review. Studies are shown in relation to the publication period and the different categories referring to the intervention. A few studies are from pear orchards. *: record date 16 May 18 plus one article from 2019.</p>
Full article ">Figure 2
<p>Floral resources to promote natural enemies in apple orchards. (<b>a</b>) Faba bean with extrafloral glands situated in the black spot on the Stipulae. Faba bean was experimented as cover crop. (<b>b</b>) Flower strip composed of perennial plant species between tree rows. Fotos: Annette Herz, JKI Darmstadt © (<b>a</b>), Simon Feiertag, JKI Darmstadt © (<b>b</b>).</p>
Full article ">Figure 3
<p>Management of inter-row perennial flower strips in an apple orchard by using a specific mulching device. The flower strip is about 0.5 m wide, whereas the adjacent vegetation is cut down frequently to reduce establishment of voles and competition for water and nutrients. Foto: Simon Feiertag, JKI Darmstadt ©.</p>
Full article ">
2194 KiB  
Article
Getting More Power from Your Flowers: Multi-Functional Flower Strips Enhance Pollinators and Pest Control Agents in Apple Orchards
by Alistair John Campbell, Andrew Wilby, Peter Sutton and Felix Wäckers
Insects 2017, 8(3), 101; https://doi.org/10.3390/insects8030101 - 20 Sep 2017
Cited by 84 | Viewed by 9761
Abstract
Flower strips are commonly recommended to boost biodiversity and multiple ecosystem services (e.g., pollination and pest control) on farmland. However, significant knowledge gaps remain regards the extent to which they deliver on these aims. Here, we tested the efficacy of flower strips that [...] Read more.
Flower strips are commonly recommended to boost biodiversity and multiple ecosystem services (e.g., pollination and pest control) on farmland. However, significant knowledge gaps remain regards the extent to which they deliver on these aims. Here, we tested the efficacy of flower strips that targeted different subsets of beneficial arthropods (pollinators and natural enemies) and their ecosystem services in cider apple orchards. Treatments included mixes that specifically targeted: (1) pollinators (‘concealed-nectar plants’); (2) natural enemies (‘open-nectar plants’); or (3) both groups concurrently (i.e., ‘multi-functional’ mix). Flower strips were established in alleyways of four orchards and compared to control alleyways (no flowers). Pollinator (e.g., bees) and natural enemy (e.g., parasitoid wasps, predatory flies and beetles) visitation to flower strips, alongside measures of pest control (aphid colony densities, sentinel prey predation), and fruit production, were monitored in orchards over two consecutive growing seasons. Targeted flower strips attracted either pollinators or natural enemies, whereas mixed flower strips attracted both groups in similar abundance to targeted mixes. Natural enemy densities on apple trees were higher in plots containing open-nectar plants compared to other treatments, but effects were stronger for non-aphidophagous taxa. Predation of sentinel prey was enhanced in all flowering plots compared to controls but pest aphid densities and fruit yield were unaffected by flower strips. We conclude that ‘multi-functional’ flower strips that contain flowering plant species with opposing floral traits can provide nectar and pollen for both pollinators and natural enemies, but further work is required to understand their potential for improving pest control services and yield in cider apple orchards. Full article
(This article belongs to the Special Issue Arthropod Pest Control in Orchards and Vineyards)
Show Figures

Figure 1

Figure 1
<p>Effects of flower strips on flower-visiting pollinators in orchard alleyways. We detected significant effects of treatment (control, concealed-nectar, mixed, and open-nectar) on pollinator richness in either study year (<b>a</b>,<b>b</b>); an effect of the interaction between treatment and sampling month (June, July, and August) on eusocial bee abundance in 2012 (<b>c</b>); an effect of treatment on eusocial bee abundance in 2013 (<b>d</b>); and an effect of treatment on solitary bees in 2012 (<b>e</b>); but not 2013 (<b>f</b>). Error bars show standard errors and asterisks show level of significance (NS = <span class="html-italic">p</span> &gt; 0.05, * = <span class="html-italic">p</span> &lt; 0.05, ** = <span class="html-italic">p</span> &lt; 0.01, *** = <span class="html-italic">p</span> &lt; 0.001) reported in LRTs (see <a href="#insects-08-00101-t001" class="html-table">Table 1</a> and main text for details).</p>
Full article ">Figure 2
<p>Effects of flower strips on flower-visiting natural enemies in orchard alleyways. We detected a significant effect of treatment on aphidophagous taxa in 2013 but not in 2012 (<b>c</b>,<b>d</b>); Other natural enemies and overall natural enemy richness were affected by the interaction between treatment (control, concealed-nectar, mixed, and open-nectar) and sampling month (June, July, and August) in 2012 (<b>a</b>,<b>e</b>); but by treatment only in 2013 (<b>b</b>,<b>f</b>). Error bars show standard errors and asterisks show level of significance (NS = <span class="html-italic">p</span> &gt; 0.05, * = <span class="html-italic">p</span> &lt; 0.05, ** = <span class="html-italic">p</span> &lt; 0.01, *** = <span class="html-italic">p</span> &lt; 0.001) reported in LRTs (see <a href="#insects-08-00101-t001" class="html-table">Table 1</a> and main text for details).</p>
Full article ">Figure 3
<p>Effects of flower strips on natural enemies and aphid pests in apple trees (number of individuals/colonies per fifty branches). We detected no effect of treatment (control, concealed-nectar, mixed, and open-nectar) on aphidophagous natural enemies (hoverflies, lacewings, earwigs and ladybirds; (<b>a</b>,<b>b</b>)) or pest aphid densities in either year (<b>e</b>,<b>f</b>); but significant effects of treatment on other natural enemy abundance (non-syrphid flies, parasitoid wasps, bugs and non-coccinellid beetles; (<b>c</b>,<b>d</b>)). Error bars show standard errors and asterisks show level of significance (NS = <span class="html-italic">p</span> &gt; 0.05, * = <span class="html-italic">p</span> &lt; 0.05, ** = <span class="html-italic">p</span> &lt; 0.01, *** = <span class="html-italic">p</span> &lt; 0.001) reported in LRTs (see <a href="#insects-08-00101-t002" class="html-table">Table 2</a> and main text for details).</p>
Full article ">Figure 4
<p>Mean (±SE) predation rate (0 = no predation and 1 = complete removal) of sentinel moth eggs in apple trees adjacent to different flower mixtures and control plots in 2013. (<b>a</b>). Inset photographs (<b>b</b>) show coccinellid larva feeding on eggs and example of card in apple foliage.</p>
Full article ">Figure 5
<p>Effects of flower strips on fruit yield and fruit quality (size and weight) in orchards. We detected no effect of treatment (control, concealed-nectar, mixed, and open-nectar) on fruit yield in either study year (<b>a</b>,<b>c</b>); or on fruit size (<b>b</b>) and weight (<b>d</b>) in 2013. Error bars show standard errors.</p>
Full article ">
688 KiB  
Review
Ecosystem-Based Incorporation of Nectar-Producing Plants for Stink Bug Parasitoids
by Glynn Tillman
Insects 2017, 8(3), 65; https://doi.org/10.3390/insects8030065 - 24 Jun 2017
Cited by 12 | Viewed by 4749
Abstract
Adult parasitoids of pest insects rely on floral resources for survival and reproduction, but can be food-deprived in intensively managed agricultural systems lacking these resources. Stink bugs are serious pests for crops in southwest Georgia. Provisioning nectar-producing plants for parasitoids of stink bugs [...] Read more.
Adult parasitoids of pest insects rely on floral resources for survival and reproduction, but can be food-deprived in intensively managed agricultural systems lacking these resources. Stink bugs are serious pests for crops in southwest Georgia. Provisioning nectar-producing plants for parasitoids of stink bugs potentially can enhance biocontrol of these pests. Knowledge of spatial and temporal availability and distribution of stink bugs in host plants is necessary for appropriate timing and placement of flowering plants in agroecosystems. Stink bugs move between closely associated host plants throughout the growing season in response to deteriorating suitability of their host plants. In peanut-cotton farmscapes, stink bugs develop in peanut, and subsequently the adults disperse into adjacent cotton. Parasitism of Nezara viridula (L.) adults by Trichopoda pennipes (F.) at the peanut-cotton interface was significantly higher in cotton with a strip of milkweed or buckwheat between the two crops than in cotton alone. Milkweed and buckwheat also provided nectar to a wide range of insect pollinators. Monarch butterflies fed on milkweed. When placed between peanut and cotton, a strip of soybean was an effective trap crop for cotton, reducing economic damage. Incorporation of buckwheat near soybean enhanced parasitism of Euschistus servus (Say) eggs by Telenomus podisi Ashmead in cotton. In conclusion, nectar provision enhances biocontrol of stink bugs, acts together with other management tactics for stink bug control, and aids in conservation of natural enemies, insect pollinators, and the monarch butterfly. Full article
(This article belongs to the Special Issue Habitat Management in Agroecosystems)
Show Figures

Figure 1

Figure 1
<p>Nectar-provision: (<b>a</b>) <span class="html-italic">Trichopoda pennipes</span> and ladybeetle adult feeding on milkweed nectar with a monarch butterfly larva feeding on leaf; (<b>b</b>) <span class="html-italic">Trichopoda pennipes</span> feeding on buckwheat nectar.</p>
Full article ">
Back to TopTop