| Literature DB >> 32626611 |
Emily K Meineke1, Carlo Tomasi2, Song Yuan3, Kathleen M Pryer4.
Abstract
PREMISE: Despite the economic significance of insect damage to plants (i.e., herbivory), long-term data documenting changes in herbivory are limited. Millions of pressed plant specimens are now available online and can be used to collect big data on plant-insect interactions during the Anthropocene.Entities:
Keywords: Anthropocene; climate change; herbarium; insects; machine learning; species interactions
Year: 2020 PMID: 32626611 PMCID: PMC7328658 DOI: 10.1002/aps3.11369
Source DB: PubMed Journal: Appl Plant Sci ISSN: 2168-0450 Impact factor: 1.936
FIGURE 1Herbarium specimens exhibiting a range of herbivory types made by different insect taxa for which recognition was automated in this study, including examples of leaf interior feeding and leaf margin feeding (A), stippling and serpentine mines (B), blotch mines (C), and skeletonization (D).
Sampling of a priori hypotheses that are of broad interest in ecology. From left to right, we list predictions made from these hypotheses using limited available data, the data gap that could be filled by large‐scale herbivory data sets derived using machine learning algorithms applied to herbarium specimens, and relevant publications pointing to the need for big data to more fully assess predictions.
| Hypothesis | Prediction(s) | Data gap to be filled | Relevant publication(s) |
|---|---|---|---|
| Herbivory rates depend on latitude | Herbivory is elevated at lower latitudes. | Limited herbivory data across latitudes | Moles et al., |
| Herbivory results in a major transfer of energy and nutrients from primary producers to consumers |
Herbivores consume about 5% of all leaf tissue, representing a small transfer of energy and nutrients. vs. Herbivores consume 10–20% of all leaf tissue, representing a large transfer of energy and nutrients. | Limited herbivory data worldwide and across the plant phylogeny |
Turcotte et al., vs. Coley et al., Cyr and Face., Cebrian and Lartigue, |
| Herbivory rates vary among plant lineages | Ferns incur less herbivory than angiosperms. | Limited herbivory data across the plant phylogeny | Cooper‐Driver, |
| Herbivory rates depend on plant growth form and size | Large plants are more “apparent” to herbivores and are thus are eaten at higher rates than smaller plants. | Limited standardized herbivory data across plant growth forms | Feeny, |
| Herbivory intensity has changed due to climate change |
Herbivory has increased where winters are warming. Herbivory has decreased where temperatures newly exceed insect thermal maxima. | Spotty monitoring of insects/herbivory before and after the acceleration of climate change in the 1970s | Meineke et al., |
| Herbivory intensity has changed due to urbanization |
Effects of urban warming on insect herbivory/diversity depend on latitude. In general, urbanization reduces damage by chewing herbivores. | Poor long‐term monitoring of how building cities affects insects/herbivory |
Diamond et al., Kozlov et al., Meineke and Davies, |
| Invasive plants experience “natural enemy release” | Invasive species escape herbivory in introduced habitats but accumulate herbivores in novel habitats over time. | Limited data on how much introduced species are damaged by herbivores throughout the invasion process | Zangerl and Berenbaum, |
Number of leaf‐damage rectangles annotated for each category and species in our data set. The last two columns denote “no damage” categories. Each rectangle was drawn to enclose the leaf damage tightly.
| Species | Margin feeding | Interior feeding | Skeletonization | Stippling | Blotch mines | Serpentine mines | Normal margin | Normal interior |
|---|---|---|---|---|---|---|---|---|
|
| 39 | 28 | 8 | 0 | 11 | 11 | 46 | 25 |
|
| 456 | 616 | 215 | 184 | 28 | 18 | 206 | 223 |
FIGURE 2A collage of all true‐positive detections for interior leaf damage (A) and leaf margin damage (B) in 22 test images. A true positive is an instance of damage that was annotated by a human and detected by the detector. In these images, dashed boxes represent human annotations, and solid boxes represent detector results. Green boxes represent interior feeding, and red boxes represent margin feeding.
FIGURE 3A collage of all false‐negative detections for interior leaf damage (A) and leaf margin damage (B) in 22 test images. A false negative is an instance of damage that was annotated by a human but was missed by the detector. In these images, dashed boxes represent human annotations, and solid boxes represent detector results. Green boxes represent interior feeding, and red boxes represent margin feeding.
FIGURE 4A collage of all false‐positive detections for interior leaf damage (A) and leaf margin damage (B) in 22 test images. A false positive is an image region that was detected by the algorithm but not marked as either interior feeding or margin feeding by the human annotator. In these images, dashed boxes represent human annotations, and solid boxes represent detector results. Green boxes represent interior feeding, and red boxes represent margin feeding.
Confusion matrix with correct/incorrect predictions made by our classifier on the 1105 sample boxes (of size 224 × 224 pixels) in our test set. Each rectangle counted in Table 2 produced a variable number of sample boxes (see text for details).
| Margin feeding | Interior feeding | Skeletonization | Stippling | Blotch mines | Serpentine mines | Normal margin | Normal interior | |
|---|---|---|---|---|---|---|---|---|
|
|
| 13 | 0 | 1 | 0 | 0 | 14 | 0 |
|
| 4 |
| 2 | 0 | 0 | 0 | 0 | 0 |
|
| 1 | 1 |
| 2 | 2 | 0 | 0 | 0 |
|
| 1 | 0 | 3 |
| 2 | 0 | 0 | 1 |
|
| 5 | 3 | 81 | 13 |
| 0 | 0 | 1 |
|
| 0 | 0 | 1 | 0 | 1 |
| 0 | 1 |
|
| 39 | 0 | 0 | 0 | 0 | 0 |
| 1 |
|
| 1 | 0 | 0 | 1 | 0 | 0 | 6 |
|
Boldfaced numbers show correct classifications.