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29 results for “invasive species control”

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zenodo40/100

Figure 3 in Getting to a decision: using structured decision-making to gain consensus on approaches to invasive species control

Figure 3. Total multi-attribute utility including all weighted objectives for responding to smallmouth bass in Cultus Lake, BC, across all management activities. Each utility was on a scale from 0-1, so the multi-attribute scale also ranges from 0–1.

opencc-by-4.0Jul 2020View details →
zenodo40/100

Figure 1 in Getting to a decision: using structured decision-making to gain consensus on approaches to invasive species control

Figure 1. Steps involved in structured decision-making. Steps can be re-evaluated at any point; responses should be re-evaluated once new data is gathered following implementation. Adapted from Liu and Cook (2016).

opencc-by-4.0Jul 2020View details →
zenodo40/100

Figure 2 in Getting to a decision: using structured decision-making to gain consensus on approaches to invasive species control

Figure 2. Calculated utility of avoiding fish species at-risk and not at-risk of extirpation in Cultus Lake, BC, across all combinations of smallmouth bass control. Utility is presented on a scale from 0–1.

opencc-by-4.0Jul 2020View details →
zenodo40/100

Figure 1 in Integrating landscape simulation models with economic and decision tools for invasive species control

Figure 1. Example state and transition simulation model for an invasive species. Landscape change is captured by defining the processes (transitions) that can move a cell from one state to another. These include both natural transitions (e.g., species dispersal, establishment, growth, fire, disturbance) and management transitions (e.g., inventory, treatment, and other activities related to invasion control). In this example, modified from Jarnevich et al. (2015), each box represents the state of a simulation cell with respect to invasive species cover (uninvaded, <5% cover, 5–50% cover, or> 50% cover; left to right) and detection (undetected or detected; top to bottom). The different color-coded arrows represent different types of transitions including growth (invasion, establishment, spread), detection (failure and success), and management (treatment and maintenance failure and success). Solid lines represent success; dotted lines represent failure.

opencc-by-4.0Nov 2018View details →
zenodo40/100

Figure 1 Aceria alhagi n in A new Aceria species (Acari:Trombidiformes: Eriophyoidea) from West Asia, a potential biological control agent for the invasive weed camelthorn, Alhagi maurorum Medik. (Leguminosae)

Figure 1 Aceria alhagi n.sp.: AD – Antero-dorsal mite; AL – Antero-lateral view of mite; CG – Coxigenital region of female; em – Empodium; GM – Genital region of male; IG – Internal female genitalia; L1 – Leg I of female; LO – Lateral opisthosoma; PM – Postero-lateral mite. Scale bar: 20μm for AD, AL,CG, GM, IG, LO, PM; 10μm for L1; 5μm for em.

opencc-by-4.0Feb 2018View details →
zenodo40/100

Figure 2 SEM images ofAceria alhagi n in A new Aceria species (Acari:Trombidiformes: Eriophyoidea) from West Asia, a potential biological control agent for the invasive weed camelthorn, Alhagi maurorum Medik. (Leguminosae)

Figure 2 SEM images ofAceria alhagi n. sp.: A – prodorsal shield; B – tarsal empodia on legs I and II; C – ventral view of coxigenital area of female; D – ventral view of coxigenital area of male.

opencc-by-4.0Feb 2018View details →
zenodo40/100

Short-term effects of the control of an invasive plant Asclepias syriaca: secondary invasion of other neophytes instead of the recovery of native species

<p>Data sets to article: &quot;Short-term effects of the control of an invasive plant <em>Asclepias syriaca</em>: secondary invasion of other neophytes instead of the recovery of native species&quot;.</p> <p>We studied the impact of <em>Asclepias syriaca</em>, a non-native herb species, on basic soil attributes and vegetation composition in sandy grasslands and the effect of mechanical control of this species. &nbsp;The <em>Asclepias </em>invasion changed the vegetation composition, but not the studied soil attributes. The shot-term cutting suppressed <em>Asclepias</em>, but instead of the recovery of native species, secondary invasion by other alien species occurred.</p>

opencc-by-4.0Dec 2022View details →
dryad40/100

Data from: Selectivity of invasive species suppression efforts influences control efficacy

Open the record for dataset details and reuse information.

publicDec 2024View details →
zenodo36/100

Figure 3 Alhagi maurorum, plant with typical Aceria alhagi n in A new Aceria species (Acari:Trombidiformes: Eriophyoidea) from West Asia, a potential biological control agent for the invasive weed camelthorn, Alhagi maurorum Medik. (Leguminosae)

Figure 3 Alhagi maurorum, plant with typical Aceria alhagi n. sp. symptoms where the shoot tips

opencc-by-4.0Feb 2018View details →
zenodo32/100

FIGURES 5–13 in Description of a new species of Anagyrus Howard (Hymenoptera: Chalcidoidea: Encyrtidae), a promising biological control agent of the invasive Madeira mealybug, Phenacoccus madeirensis Green (Hemiptera: Sternorrhyncha: Pseudococcidae)

FIGURES 5–13. Anagyrus amnestos sp. n.: 5. Female head, frontal view (slide preparation); 6. Male head, frontal view (slide preparation); 7. Antenna, female; 8. Antenna, male; 9. Head and mesosoma, dorsal view; 10. Fore wing, female; 11. Fore wing, male; 12. Female genitalia; 13. Male genitalia.

opennotspecifiedDec 2013View details →
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FIGURES 20–27 in Description of a new species of Anagyrus Howard (Hymenoptera: Chalcidoidea: Encyrtidae), a promising biological control agent of the invasive Madeira mealybug, Phenacoccus madeirensis Green (Hemiptera: Sternorrhyncha: Pseudococcidae)

FIGURES 20–27. Anagyrus kamali: 20. Female, dorsal view; 21. Female, lateral view; 22. Antenna, female; 23. Antenna, male; 24. Male, dorsal view; 25. Male, lateral view; 26. Head and mesosoma, dorsal view; 27. Fore wing, female.

opennotspecifiedDec 2013View details →
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FIGURES 1–4 in Description of a new species of Anagyrus Howard (Hymenoptera: Chalcidoidea: Encyrtidae), a promising biological control agent of the invasive Madeira mealybug, Phenacoccus madeirensis Green (Hemiptera: Sternorrhyncha: Pseudococcidae)

FIGURES 1–4. Anagyrus amnestos sp. n.: 1. Female, dorsal view; 2. Female, lateral view; 3. Male, dorsal view; 4. Female, dorsal view of head, and antenna.

opennotspecifiedDec 2013View details →
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FIGURES 14–19 in Description of a new species of Anagyrus Howard (Hymenoptera: Chalcidoidea: Encyrtidae), a promising biological control agent of the invasive Madeira mealybug, Phenacoccus madeirensis Green (Hemiptera: Sternorrhyncha: Pseudococcidae)

FIGURES 14–19. Anagyrus agraensis: 14. Female, dorsal view; 15. Female, lateral view; 16. Head and mesosoma, dorsal view; 17. Antenna, female; 18. Antenna, male; 19. Fore wing, female.

opennotspecifiedDec 2013View details →
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FIGURES 3–8. Tamarixia schina, female. 3. Habitus. 4. Forewing. 5. Antenna. 6. Head, frontal view. 7 in Two new species of Ta m a r i x i a (Hymenoptera: Eulophidae) from Chile and Australia, established as biological control agents of invasive psyllids (Hemiptera: Calophyidae, Triozidae) in California

FIGURES 3–8. Tamarixia schina, female. 3. Habitus. 4. Forewing. 5. Antenna. 6. Head, frontal view. 7. Mesosoma, lateral

opennotspecifiedDec 2011View details →
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FIGURES 1, 2. 1 in Two new species of Ta m a r i x i a (Hymenoptera: Eulophidae) from Chile and Australia, established as biological control agents of invasive psyllids (Hemiptera: Calophyidae, Triozidae) in California

FIGURES 1, 2. 1. Damage caused by Calophya schini on Schinus molle. 2. Damage caused by Trioza eugeniae on Syzygium paniculatum. Photos by Jack Kelly Clark, courtesy University of California Statewide IPM Program. Copyrighted by the Regents of the University of California.

opennotspecifiedDec 2011View details →
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FIGURES 13–16. Tamarixia dahlsteni, female. 13. Head, frontal view. 14. Mesosoma, lateral view. 15. Mesosoma, dorsal view. 16 in Two new species of Ta m a r i x i a (Hymenoptera: Eulophidae) from Chile and Australia, established as biological control agents of invasive psyllids (Hemiptera: Calophyidae, Triozidae) in California

FIGURES 13–16. Tamarixia dahlsteni, female. 13. Head, frontal view. 14. Mesosoma, lateral view. 15. Mesosoma, dorsal view. 16. Propodeum.

opennotspecifiedDec 2011View details →
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FIGURES 9–12. Tamarixia dahlsteni. 9. Habitus, female. 10. Forewing, female. 11. Antenna, female. 12 in Two new species of Ta m a r i x i a (Hymenoptera: Eulophidae) from Chile and Australia, established as biological control agents of invasive psyllids (Hemiptera: Calophyidae, Triozidae) in California

FIGURES 9–12. Tamarixia dahlsteni. 9. Habitus, female. 10. Forewing, female. 11. Antenna, female. 12. Head and antennae, male.

opennotspecifiedDec 2011View details →
zenodo32/100

Supplementary material 3 from: Anđelković AA, Lawson Handley L, Marchante E, Adriaens T, Brown PMJ, Tricarico E, Verbrugge LNH (2022) A review of volunteers' motivations to monitor and control invasive alien species. NeoBiota 73: 153-175. https://doi.org/10.3897/neobiota.73.79636

List of recommendations for designing projects to ensure maximum recruitment and volunteer retention extracted from the studies used in the analysis (for their full references, please see Suppl. material 1) and their link to our recommendations

opencc-zeroMay 2022View details →
dryad28/100

Data from: Species richness and interacting factors control invasibility of a marine community

Anthropogenic vectors have moved marine species around the world leading to increased invasions and expanded species' ranges. The biotic resistance hypothesis of Elton (in The ecology of invasions by animals and plants, 1958) predicts that more diverse communities should have greater resistance to invasions, but experiments have been equivocal. We hypothesized that species richness interacts with other factors to determine experimental outcomes. We manipulated species richness, species composition (native and introduced) and availability of bare space in invertebrate assemblages in a marina in Monterey, CA. Increased species richness significantly interacted with both initial cover of native species and of all organisms to collectively decrease recruitment. Although native species decreased recruitment, introduced species had a similar effect, and we concluded that biotic resistance is conferred by total species richness. We suggest that contradictory conclusions in previous studies about the role of diversity in regulating invasions reflect uncontrolled variables in those experiments that modified the effect of species richness. Our results suggest that patches of low diversity and abundance may facilitate invasions, and that such patches, once colonized by non-indigenous species, can resist both native and non-indigenous species recruitment.

opencc-zeroDec 2014View details →
zenodo28/100

Supplementary material 1 from: Anđelković AA, Lawson Handley L, Marchante E, Adriaens T, Brown PMJ, Tricarico E, Verbrugge LNH (2022) A review of volunteers' motivations to monitor and control invasive alien species. NeoBiota 73: 153-175. https://doi.org/10.3897/neobiota.73.79636

List of the studies used in the analysis

opencc-zeroMay 2022View details →

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International Brain Laboratory public data

The International Brain Laboratory public data releases expose standardized mouse decision-making experiments, including Neuropixels recordings, widefield calcium imaging, behavior, and session metadata accessed through the ONE API.

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Last verified 2026-04-29Open record