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Clarify taxonomic considerations in combining data, add direct links for NEON resources

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  1. README.md +22 -38
README.md CHANGED
@@ -63,10 +63,10 @@ Each image is accompanied by trait annotations and measurements, providing valua
63
  ## Dataset Structure
64
 
65
  ```
66
- /group_images
67
  IMG_<id>.png
68
  ...
69
- /individual_specimens
70
  IMG_<id>_specimen_<number>_<taxonID>_<individualID>.png
71
  ...
72
  images_metadata.csv
@@ -100,17 +100,18 @@ README.md
100
  - `coords_elytra_max_length`: X and Y coordinate pairs defining the endpoints of the maximum elytral length measurement. Measured from the midpoint of the elytro-pronotal suture (junction between pronotum and elytra) to the midpoint of the elytral apex (posterior terminus of the elytra). Ex: `"[[3865.5, 1245.87, 3881.25, 1045.81]]"`.
101
  - `coords_basal_pronotum_width`: X and Y coordinate pairs defining the endpoints of the basal pronotal width measurement at the elytro-pronotal junction. Ex: `"[[3922.92, 1046.2, 3872.53, 1035.06]]"`.
102
  - `coords_elytra_max_width`: X and Y coordinate pairs defining the endpoints of the maximum elytral width measurement. Represents the greatest transverse distance across both elytra, measured orthogonal to the elytral length axis. Ex: `"[[3960.08, 1145.79, 3814.38, 1123.85]]"`.
103
- - `px_scalebar`: Euclidean distance between coordinate endpoints of the reference scalebar (`coords_scalebar`) expressed in pixels, measured to ____ precision.
104
- - `px_elytra_max_length`: Euclidean distance between coordinate endpoints of the maximum elytral length (`coords_elytra_max_length`) expressed in pixels.
105
- - `px_basal_pronotum_width`: Euclidean distance between coordinate endpoints of the basal pronotal width (`coords_basal_pronotum_width`) expressed in pixels.
106
- - `px_elytra_max_width`: Euclidean distance between coordinate endpoints of the maximum elytral width (`coords_elytra_max_width`) expressed in pixels.
107
  - `cm_scalebar`: Calibrated length of the reference scalebar in centimeters. Constant value of 1.0 cm as this represents the standard reference scale used for all measurements.
108
- - `cm_elytra_max_length`: Calibrated maximum elytral length in centimeters<sup>[1](#footnote1)</sup>, calculated by converting pixel measurements using the scalebar calibration factor.
109
- - `cm_basal_pronotum_width`: Calibrated basal pronotal width in centimeters<sup>[1](#footnote1)</sup> at the elytro-pronotal suture, calculated by converting pixel measurements using the scalebar calibration factor.
110
- - `cm_elytra_max_width`: Calibrated maximum elytral width in centimeters<sup>[1](#footnote1)</sup>, representing the greatest transverse dimension across the fused elytra, calculated by converting pixel measurements using the scalebar calibration factor.
111
 
 
112
 
113
- <a name="footnote1">1</a>: The measurement is up to 3 decimal places. To get measurements with more numerical precision (i.e. additional decimal places), use this equation: `cm_<measurement>` = `px_<measurement>`/`px_scalebar`.
114
 
115
 
116
  ## Dataset Creation
@@ -123,7 +124,7 @@ Ground beetles (Coleoptera: Carabidae) serve as critical bioindicators for ecosy
123
 
124
  ### Source Data
125
 
126
- The specimens come from the PUUM [NEON site](https://www.neonscience.org/field-sites/explore-field-sites). For more information about general NEON data, please see their [Ground beetles sampled from pitfall traps page](https://data.neonscience.org/data-products/DP1.10022.001).
127
 
128
  Our team photographed the beetles in 2025, using Canon EOS DSLR (model 7D).
129
 
@@ -144,7 +145,7 @@ After imaging all the specimens, the data curation team segmented the individual
144
 
145
  #### Annotation process
146
 
147
- Trait annotations were produced using **TORAS** (Trait Observation and Recording Annotation System, a high-precision tool designed for detailed morphological measurements on high-resolution images of pinned beetle specimens. Annotators manually placed coordinate pairs marking the endpoints of key anatomical landmarks: the 1 cm reference scalebar (`coords_scalebar`), maximum elytral length (`coords_elytra_max_length`), basal pronotal width at the elytro-pronotal junction (`coords_basal_pronotum_width`), and maximum elytral width (`coords_elytra_max_width`). From these coordinates, Euclidean distances were computed in pixels (`px_scalebar`, `px_elytra_max_length`, `px_basal_pronotum_width`, `px_elytra_max_width`) and converted to centimeters using the *scalebar calibration factor* (cm_scalebar = 1.0 cm). Annotations were performed exclusively on dorsal-view images to maximize visibility of diagnostic morphological traits. Rigorous quality control ensured that each image met predefined standards for focus, illumination, and label legibility.
148
 
149
  For validation, a subset of 64 specimens was measured physically with digital calipers by three independent annotators. These same specimens were then used for two complementary analyses:
150
  1. **Inter-annotator agreement**, assessing consistency among the three caliper-based measurements (average RMSE ≈ 0.024 cm, R² ≈ 0.94); and
@@ -152,28 +153,20 @@ For validation, a subset of 64 specimens was measured physically with digital ca
152
 
153
  Together, these results confirm that TORAS measurements closely reproduce manual ground-truth measurements while maintaining high inter-annotator consistency, establishing the reliability and reproducibility of the annotation process for quantitative morphological trait extraction.
154
 
155
- <!-- Trait annotations were generated using the TORAS (Trait Observation and Recording Annotation System) tool for precise measurements on high-resolution images of pinned specimens. Annotators manually marked coordinate pairs defining the endpoints of key morphological features: the 1 cm reference scalebar (`coords_scalebar`), maximum elytral length (`coords_elytra_max_length`), basal pronotal width at the elytro-pronotal junction (`coords_basal_pronotum_width`), and maximum elytral width (`coords_elytra_max_width`). Euclidean distances were calculated in pixels (`px_scalebar`, `px_elytra_max_length`, `px_basal_pronotum_width`, `px_elytra_max_width`) and calibrated to centimeters (`cm_scalebar` = 1.0 constant; others converted using the scalebar calibration factor). Annotations focused on dorsal views to ensure visibility of taxonomically relevant features, with quality control to verify focus, lighting, and label legibility. Digital measurements were validated against manual caliper-based measurements, achieving sub-millimeter precision with transparent error quantification. A subset of 64 specimens was annotated independently by three annotators to assess inter-annotator agreement, and the results demonstrated high consistency (average RMSE ≈ 0.024 cm, R² ≈ 0.94). For validating TORAS as a tool, TORAS-based digital measurements were validated against manual caliper measurements on physical specimens, achieving sub-millimeter precision (RMSE ≈ 0.015 cm; R² > 0.97).-->
156
-
157
  #### Who are the annotators?
158
 
159
- - Annotations were conducted by a team of researchers and students from the Experiential Introduction to AI and Ecology Course, jointly organized by the Imageomics Institute and the AI and Biodiversity Change (ABC) Global Climate Center.
160
  - Primary contributors include S. M. Rayeed, Mridul Khurana, Alyson East, and Elizabeth G. Campolongo, with additional contributions from Samuel Stevens, Iuliia Zarubiieva, Jiaman (Lisa) Wu, and Scott C. Lowe. Evan D. Donso, a NEON field technician, assisted with specimen handling, data collection, and trait measurement using calipers.
161
- - All annotation work was performed under the supervision of advisors Graham W. Taylor and Sydne Record. Fieldwork and imaging were carried out at the NEON PUUM site between January 15–29, 2025.
162
-
163
- <!--
164
- Annotations were performed by a team of researchers and students participating in the Experiential Introduction to AI and Ecology Course organized by the Imageomics Institute and the AI and Biodiversity Change (ABC) Global Climate Center. Key contributors included S M Rayeed, Mridul Khurana, Alyson East, and Elizabeth G. Campolongo. other co-authors are Samuel Stevens, Iuliia Zarubiieva, Jiaman (Lisa) Wu, Isadora E. Fluck, Scott C. Lowe, Evan D Donso -- with oversight from advisors Graham W. Taylor and Sydne Record. The fieldwork and imaging occurred at the PUUM site in Hawaii from January 15-29, 2025.
165
- -->
166
-
167
- <!-- This section describes the people or systems who created the annotations. -->
168
 
169
 
170
  ### Personal and Sensitive Information
171
 
172
- Our data does not contain any personal or sensitive Information.
173
 
174
  ## Considerations for Using the Data
175
 
176
- This dataset comprises pinned beetle specimens collected from the NEON PUUM site between 2018 and 2024, representing 14 identified species within the Carabidae family. While *taxonomically and geographically constrained*, the dataset provides **high-quality, standardized imagery and trait data suitable for AI, computer vision, and ecological modeling applications**. Each specimen image is a **high-resolution dorsal view**, optimized for automated trait extraction, object detection, and segmentation. ***No ventral or lateral views are included***. Trait measurements—such as elytral length and width—are fully calibrated using a 1 cm reference scalebar and have been validated to sub-millimeter precision, ensuring reliability for quantitative analyses. Specimens can be linked to NEON’s environmental and ecological data streams, including climate, vegetation, and co-located taxa (e.g., plants, mammals, and birds), via shared identifiers such as `plotID`, `trapID`, `plotTrapID`, and `collectDate`. For programmatic integration, users may access broader NEON metadata through APIs using individualID or sampleCode. *All images adhere to FAIR data principles*, supporting findability, accessibility, interoperability, and reusability across biodiversity and ecological research platforms. Overall, this dataset serves as a robust foundation for trait-based ecological modeling, species-level computer vision tasks, and integration with multi-domain NEON data, provided users account for its limited geographic and taxonomic scope.
177
 
178
  <!--
179
  Things to consider while working with the dataset. For instance, maybe there are hybrids and they are labeled in the `hybrid_stat` column, so to get a subset without hybrids, subset to all instances in the metadata file such that `hybrid_stat` is _not_ "hybrid".
@@ -181,28 +174,19 @@ Things to consider while working with the dataset. For instance, maybe there are
181
 
182
  ## Bias, Risks, and Limitations
183
 
184
- The dataset exhibits several inherent biases and limitations that should be considered when interpreting results or developing models. **Geographically**, it is limited to a single tropical site (PUUM), which is not representative of the diverse environmental conditions found across the continental United States, such as deserts, temperate forests, or taiga ecosystems. **Taxonomically**, the dataset includes only 14 of more than 40,000 known carabid species, with a long-tailed distribution dominated by a few genera — primarily *Mecyclothorax* and *Trechus* — thus underrepresenting the broader diversity of the Carabidae family. Sampling bias arises from the exclusive use of pitfall traps, which preferentially capture ground-active and diurnal beetles while largely excluding arboreal or flying taxa. There is also **limited coverage of intraspecific variation**, as specimens do not span a wide range of geographic clines, life stages, or microhabitats. From a technical perspective, *imaging artifacts such as minor glare or partial label obstruction* may persist despite quality control procedures. The dataset’s **scale — with 1,614 images** — makes it relatively small for standalone large-scale machine learning applications without data augmentation. Finally, ***there is a risk of misuse***, as AI models trained solely on this dataset may exhibit poor generalization when applied to other regions, species, or imaging conditions, underscoring the importance of cross-dataset validation and ecological context awareness.
185
 
186
  <!-- This section is meant to convey both technical and sociotechnical limitations. Could also address misuse, malicious use, and uses that the dataset will not work well for. For instance, if your data exhibits a long-tailed distribution (and why). -->
187
 
188
 
189
  ### Recommendations
190
 
191
- - Mitigating Geographic Bias: To address the limited geographic scope of the Hawai‘i dataset, combine it collections from other NEON terrestrial sites across multiple domains. This integration will enable continental-scale analyses of trait–environment relationships and improve ecological generalizability across biomes.
192
- - Balancing Taxonomic Representation: To reduce the effects of the long-tailed species distribution, augment the dataset with external image and trait repositories (e.g., GBIF, iDigBio, or other museum collections). This will expand coverage across genera and species, facilitating more balanced training datasets and more robust cross-species generalization in machine learning models.
193
- - For AI and computer vision applications, researchers should augment the dataset with additional images to overcome the relatively small sample size and enhance model robustness. Expanding image diversity across species, sites, and lighting conditions will help models better capture regional morphological variation and reduce overfitting to the specific imaging setup used for the Hawai‘i specimens.
194
  - When developing or testing automated measurement pipelines, users are strongly encouraged to validate all digital trait extractions against the provided manually verified measurements. Reporting quantitative error rates (e.g., RMSE, bias, R²) will ensure transparency and maintain the high standard of reproducibility established in the original validation study, which demonstrated sub-millimeter accuracy for elytral traits.
195
  - For ecological analyses, it is essential to link specimen-level traits to NEON environmental data using identifiers such as `plotID` and `collectDate`. This enables spatially and temporally explicit studies on trait–environment relationships, including responses to climate gradients, habitat conditions, or ecological disturbances.
196
- - Researchers should avoid drawing continental-scale ecological or evolutionary inferences based solely on this dataset, as it represents a single tropical site. Broader-scale interpretations require supplementary datasets that capture geographic and taxonomic variation. Moreover, users are encouraged to consider the ethical implications of AI deployment in biodiversity monitoring and conservation, ensuring that research derived from this dataset aligns with its intended purpose of advancing ecological understanding and supporting conservation outcomes.
197
-
198
- <!--
199
- - Combine with multi-domain NEON data (vial specimens, other sites) for continental analyses
200
- - Augment with external image/trait datasets to balance long-tailed distribution
201
- - For AI applications, augment with additional images to address the small sample size and ensure models account for regional morphological variation.
202
- - Validate any automated trait extractions against the provided manual measurements, and report error rates transparently.
203
- - When linking to NEON environmental data, use identifiers like `plotID` and `collectDate` for accurate integration, enabling studies on trait-environment interactions.
204
- - Avoid using for continental-scale inferences without supplementary data, and consider ethical applications in biodiversity monitoring and conservation to align with the dataset's ecological focus.
205
- -->
206
 
207
  <!-- This section is meant to convey recommendations with respect to the bias, risk, and technical limitations. -->
208
 
 
63
  ## Dataset Structure
64
 
65
  ```
66
+ group_images/
67
  IMG_<id>.png
68
  ...
69
+ individual_specimens/
70
  IMG_<id>_specimen_<number>_<taxonID>_<individualID>.png
71
  ...
72
  images_metadata.csv
 
100
  - `coords_elytra_max_length`: X and Y coordinate pairs defining the endpoints of the maximum elytral length measurement. Measured from the midpoint of the elytro-pronotal suture (junction between pronotum and elytra) to the midpoint of the elytral apex (posterior terminus of the elytra). Ex: `"[[3865.5, 1245.87, 3881.25, 1045.81]]"`.
101
  - `coords_basal_pronotum_width`: X and Y coordinate pairs defining the endpoints of the basal pronotal width measurement at the elytro-pronotal junction. Ex: `"[[3922.92, 1046.2, 3872.53, 1035.06]]"`.
102
  - `coords_elytra_max_width`: X and Y coordinate pairs defining the endpoints of the maximum elytral width measurement. Represents the greatest transverse distance across both elytra, measured orthogonal to the elytral length axis. Ex: `"[[3960.08, 1145.79, 3814.38, 1123.85]]"`.
103
+ - `px_scalebar`: Euclidean distance between coordinate endpoints of the reference scalebar (`coords_scalebar`) expressed in pixels<sup>[1](#footnote1)</sup>.
104
+ - `px_elytra_max_length`: Euclidean distance between coordinate endpoints of the maximum elytral length (`coords_elytra_max_length`) expressed in pixels<sup>[1](#footnote1)</sup>.
105
+ - `px_basal_pronotum_width`: Euclidean distance between coordinate endpoints of the basal pronotal width (`coords_basal_pronotum_width`) expressed in pixels<sup>[1](#footnote1)</sup>.
106
+ - `px_elytra_max_width`: Euclidean distance between coordinate endpoints of the maximum elytral width (`coords_elytra_max_width`) expressed in pixels<sup>[1](#footnote1)</sup>.
107
  - `cm_scalebar`: Calibrated length of the reference scalebar in centimeters. Constant value of 1.0 cm as this represents the standard reference scale used for all measurements.
108
+ - `cm_elytra_max_length`: Calibrated maximum elytral length in centimeters<sup>[2](#footnote2)</sup>, calculated by converting pixel measurements using the scalebar calibration factor.
109
+ - `cm_basal_pronotum_width`: Calibrated basal pronotal width in centimeters<sup>[2](#footnote2)</sup> at the elytro-pronotal suture, calculated by converting pixel measurements using the scalebar calibration factor.
110
+ - `cm_elytra_max_width`: Calibrated maximum elytral width in centimeters<sup>[2](#footnote2)</sup>, representing the greatest transverse dimension across the fused elytra, calculated by converting pixel measurements using the scalebar calibration factor.
111
 
112
+ <a name="footnote1">1</a>: The measurement is up to 14 decimal places.
113
 
114
+ <a name="footnote2">2</a>: The measurement is up to 3 decimal places. To get measurements with more numerical precision (i.e. additional decimal places), use this equation: `cm_<measurement>` = `px_<measurement>`/`px_scalebar`.
115
 
116
 
117
  ## Dataset Creation
 
124
 
125
  ### Source Data
126
 
127
+ The specimens come from the [PUUM NEON site](https://www.neonscience.org/field-sites/puum). For more information about general NEON data, please see their [Ground beetles sampled from pitfall traps page](https://data.neonscience.org/data-products/DP1.10022.001).
128
 
129
  Our team photographed the beetles in 2025, using Canon EOS DSLR (model 7D).
130
 
 
145
 
146
  #### Annotation process
147
 
148
+ Trait annotations were produced using **TORAS** (Trait Observation and Recording Annotation System), a high-precision tool designed for detailed morphological measurements on high-resolution images of pinned beetle specimens. Annotators manually placed coordinate pairs marking the endpoints of key anatomical landmarks: the 1 cm reference scalebar (`coords_scalebar`), maximum elytral length (`coords_elytra_max_length`), basal pronotal width at the elytro-pronotal junction (`coords_basal_pronotum_width`), and maximum elytral width (`coords_elytra_max_width`). From these coordinates, Euclidean distances were computed in pixels (`px_scalebar`, `px_elytra_max_length`, `px_basal_pronotum_width`, `px_elytra_max_width`) and converted to centimeters using the *scalebar calibration factor* (cm_scalebar = 1.0 cm). Annotations were performed exclusively on dorsal-view images to maximize visibility of diagnostic morphological traits. Rigorous quality control ensured that each image met predefined standards for focus, illumination, and label legibility.
149
 
150
  For validation, a subset of 64 specimens was measured physically with digital calipers by three independent annotators. These same specimens were then used for two complementary analyses:
151
  1. **Inter-annotator agreement**, assessing consistency among the three caliper-based measurements (average RMSE ≈ 0.024 cm, R² ≈ 0.94); and
 
153
 
154
  Together, these results confirm that TORAS measurements closely reproduce manual ground-truth measurements while maintaining high inter-annotator consistency, establishing the reliability and reproducibility of the annotation process for quantitative morphological trait extraction.
155
 
 
 
156
  #### Who are the annotators?
157
 
158
+ - Annotations were conducted by a team of researchers and students from the Experiential Introduction to AI and Ecology Course, jointly organized by the Imageomics Institute and the AI and Biodiversity Change (ABC) Global Center.
159
  - Primary contributors include S. M. Rayeed, Mridul Khurana, Alyson East, and Elizabeth G. Campolongo, with additional contributions from Samuel Stevens, Iuliia Zarubiieva, Jiaman (Lisa) Wu, and Scott C. Lowe. Evan D. Donso, a NEON field technician, assisted with specimen handling, data collection, and trait measurement using calipers.
160
+ - All annotation work was performed under the supervision of advisors Graham W. Taylor and Sydne Record. Fieldwork and imaging were carried out at the [NEON PUUM site](https://www.neonscience.org/field-sites/puum) between January 15–29, 2025.
 
 
 
 
 
 
161
 
162
 
163
  ### Personal and Sensitive Information
164
 
165
+ Our data does not contain any personal or sensitive information.
166
 
167
  ## Considerations for Using the Data
168
 
169
+ This dataset comprises pinned beetle specimens collected from the [NEON PUUM site](https://www.neonscience.org/field-sites/puum) between 2018 and 2024, representing 14 identified species within the Carabidae family. While *taxonomically and geographically constrained*, the dataset provides **high-quality, standardized imagery and trait data suitable for AI, computer vision, and ecological modeling applications**. Each specimen image is a **high-resolution dorsal view**, optimized for automated trait extraction, object detection, and segmentation. ***No ventral or lateral views are included***. Trait measurements—such as elytral length and width—are fully calibrated using a 1 cm reference scalebar and have been validated to sub-millimeter precision, ensuring reliability for quantitative analyses. Specimens can be linked to NEON’s environmental and ecological data streams, including climate, vegetation, and co-located taxa (e.g., plants, mammals, and birds), via shared identifiers such as `plotID`, `trapID`, `plotTrapID`, and `collectDate`. For programmatic integration, users may access broader NEON metadata through the [NEON API](https://data.neonscience.org/data-api/) using `individualID` or `sampleCode`. *All images adhere to FAIR data principles*, supporting findability, accessibility, interoperability, and reusability across biodiversity and ecological research platforms. Overall, this dataset serves as a robust foundation for trait-based ecological modeling, species-level computer vision tasks, and integration with multi-domain NEON data, provided users account for its limited geographic and taxonomic scope.
170
 
171
  <!--
172
  Things to consider while working with the dataset. For instance, maybe there are hybrids and they are labeled in the `hybrid_stat` column, so to get a subset without hybrids, subset to all instances in the metadata file such that `hybrid_stat` is _not_ "hybrid".
 
174
 
175
  ## Bias, Risks, and Limitations
176
 
177
+ The dataset exhibits several inherent biases and limitations that should be considered when interpreting results or developing models. **Geographically**, it is limited to a single tropical site ([PUUM](https://www.neonscience.org/field-sites/puum)), which is not representative of the diverse environmental conditions found across the continental United States, such as deserts, temperate forests, or taiga ecosystems. **Taxonomically**, the dataset includes only 14 of more than 40,000 known carabid species, with a long-tailed distribution dominated by a few genera — primarily *Mecyclothorax* and *Trechus* — thus underrepresenting the broader diversity of the Carabidae family. Sampling bias arises from the exclusive use of pitfall traps, which preferentially capture ground-active and diurnal beetles while largely excluding arboreal or flying taxa. There is also **limited coverage of intraspecific variation**, as specimens do not span a wide range of geographic clines, life stages, or microhabitats. From a technical perspective, *imaging artifacts such as minor glare or partial label obstruction* may persist despite quality control procedures. The dataset’s **scale — with 1,614 images** — makes it relatively small for standalone large-scale machine learning applications without data augmentation. Finally, ***there is a risk of misuse***, as AI models trained solely on this dataset may exhibit poor generalization when applied to other regions, species, or imaging conditions, underscoring the importance of cross-dataset validation and ecological context awareness.
178
 
179
  <!-- This section is meant to convey both technical and sociotechnical limitations. Could also address misuse, malicious use, and uses that the dataset will not work well for. For instance, if your data exhibits a long-tailed distribution (and why). -->
180
 
181
 
182
  ### Recommendations
183
 
184
+ - Mitigating Geographic Bias: To address the limited geographic scope of the Hawai‘i dataset, consider combining it with collections from other NEON terrestrial sites across multiple domains (e.g., [2018 NEON Ethanol-preserved Ground Beetles](https://huggingface.co/datasets/imageomics/2018-NEON-beetles) and [Sentinel Beetles](https://huggingface.co/datasets/imageomics/sentinel-beetles)). This integration will enable continental-scale analyses of trait–environment relationships and improve ecological generalizability across biomes.
185
+ - Balancing Taxonomic Representation: To reduce the effects of the long-tailed species distribution, one can augment the dataset with external image and trait repositories (e.g., GBIF, iDigBio, or other museum collections). This has the potential to expand coverage across genera and species, facilitating more balanced training datasets and more robust cross-species generalization in machine learning models. When combining taxonomic data from multiple sources, be sure to align the taxonomic backbone used for labels to ensure full alignment. [TaxonoPy](https://github.com/Imageomics/TaxonoPy) was developed to accomplish this type of alignment (for [TreeOfLife-200M](https://huggingface.co/datasets/imageomics/TreeOfLife-200M)).
186
+ - For AI and computer vision applications, researchers should augment the dataset with additional images to overcome the relatively small sample size and enhance model robustness. Expanding image diversity across species, sites, and lighting conditions will help models better capture regional morphological variation and reduce overfitting to the specific imaging setup used for the Hawai‘i specimens. As noted above, different sources may use different taxonomic backbones, this should be accounted for in any compilation (e.g., with [TaxonoPy](https://github.com/Imageomics/TaxonoPy)).
187
  - When developing or testing automated measurement pipelines, users are strongly encouraged to validate all digital trait extractions against the provided manually verified measurements. Reporting quantitative error rates (e.g., RMSE, bias, R²) will ensure transparency and maintain the high standard of reproducibility established in the original validation study, which demonstrated sub-millimeter accuracy for elytral traits.
188
  - For ecological analyses, it is essential to link specimen-level traits to NEON environmental data using identifiers such as `plotID` and `collectDate`. This enables spatially and temporally explicit studies on trait–environment relationships, including responses to climate gradients, habitat conditions, or ecological disturbances.
189
+ - Researchers should avoid drawing continental-scale ecological or evolutionary inferences based solely on this dataset, as it represents a single tropical site. Broader-scale interpretations require supplementary datasets that capture geographic and taxonomic variation. As noted above, be sure to align the taxonomic naming from disparate sources (e.g., with [TaxonoPy](https://github.com/Imageomics/TaxonoPy)). Moreover, users are encouraged to consider the ethical implications of AI deployment in biodiversity monitoring and conservation, ensuring that research derived from this dataset aligns with its intended purpose of advancing ecological understanding and supporting conservation outcomes.
 
 
 
 
 
 
 
 
 
190
 
191
  <!-- This section is meant to convey recommendations with respect to the bias, risk, and technical limitations. -->
192