Abstract
Species phenology - the timing of key life events - is being altered by ongoing climate changes with yet underappreciated consequences for ecosystem stability. While flowering is generally occurring earlier, we know much less about other key processes such as the time of fruit ripening, largely due to the lack of comprehensive long-term datasets. Here we provide information on the exact date and site where seeds of 4,462 taxa were collected for the Index Seminum (seed exchange catalogue) of the Botanic Garden of the University of Coimbra, between 1926 and 2013. Seeds were collected from spontaneous and cultivated individuals across Portugal, including both native and introduced taxa. The database consists of 127,747 curated records with information on the species, or infraspecific taxa (including authority), and the day and site where seeds were collected. All records are georeferenced and provided with a confidence interval for the collection site. Taxonomy was first curated manually by in-house botanists and then harmonized according to the GBIF backbone taxonomy.
Subject terms: Plant ecology, Plant reproduction
Background & Summary
There is clear evidence that ongoing climate change is rapidly altering the timing of key recurring life events – species phenology – including plant flowering, insect emergence, or bird migration1–3. Indeed, phenological shifts are one of the first responses of organisms to environmental changes and thus one of the more sensitive biological indicators of climate changes, largely preceding other more insidious responses such as range shifts or extinctions4,5. The growing realization of the importance of phenology on ecosystem functioning and stability has triggered a revival of phenological research in recent decades, spearheaded by research on flowering phenology6–8.
While flowering is key for pollination and plant reproduction, the production of seeds and fruits is at least as important, for it is only during this short period that plants can colonize new sites or endure periods of unfavourable environmental conditions through seed dormancy9,10. Indeed, the timeframe available for fruit production is a key driver of global diversity patterns and is central to understand how these can be affected by climate change11. Furthermore, evidence shows that the drivers of fruit ripening are not necessarily the same as those driving flowering phenology12–14, rendering fruiting phenology research particularly needed14,15. Fruiting phenology has important ecological and conservation implications, as reviewed in Morellato et al.16, including the potential to create mismatches between the availability of ripe fruit and their migratory seed dispersers17,18, modulating the dispersal services available to invasive alien plant species19,20, or determining regeneration potential after wildfires21,22. All of these have a recognized potential to change the composition of future ecosystems, especially forests15,18,23. It is thus unfortunate that fruiting season information is generally not available from botanical species descriptions in the same way that flowering is.
Fruiting phenology information can be obtained by several methods. The most straightforward is the establishment of long-term phenological stations where plants are periodically inspected (ideally daily) and the date of the first ripe fruit on multiple individuals is recorded24. Alternatively, fruiting can also be identified by periodically checking fruit traps25. However, while these methods originated some of the most comprehensive and accurate datasets on fruiting phenology available to date, they require a very large commitment in terms of continued sampling effort, particularly challenging under the constraints of short funding cycles, and therefore not practical to characterize entire floras over long temporal series and large spatial scales. The compilation of metadata from biological collections, chiefly from herbarium specimens, has been a highly valuable solution e.g.8,26. However, this approach also comes with its own intrinsic biases27,28 and is particularly suited to track flowering phenology due to the taxonomic value of flowers, more commonly present in herbarium specimens than fruits29.
Although fruiting phenology studies are not uncommon, their taxonomic coverage and duration is generally low30. In particular, due to stringent trade-offs between the number of species included and effort required to monitor them31, it is possible to find some remarkably long-term datasets e.g. a single species followed for 633 years32, and some remarkably comprehensive studies e.g. 1202 species followed for 7 years33. However, to our knowledge, no study to date has managed to follow any sizeable fraction of an entire flora for more than a decade15. While new technological solutions, such as artificial intelligence and large-scale citizen science initiatives, can facilitate the automated collection of massive contemporaneous data16, they cannot offer solutions to reconstruct past phenology against which recent shifts can be compared28.
Here we explore the historical dataset of a longstanding seed exchange program that has documented fruiting phenology data for a broad spectrum of species over an extensive temporal series. This dataset was made possible by the renewed interest on the natural sciences and the proliferation of botanical gardens in the late 18th century, when some gardens established seed and plant exchange programs to expand and preserve their botanical collections and to resolve taxonomical ambiguities34. To facilitate this exchange, numerous Botanical Gardens published a list of seed species available yearly, known as Index Seminum (Latin for: Seed Catalogue), many continuing to be issued to this day35. The Index Seminum of the Botanic Garden of the University of Coimbra started in 1868 and was considerably improved in 1926 by expanding and diversifying taxa and collection range, and standardizing identification, storage and distribution of seeds36. Most importantly, there were also improvements in the gathering and storage of the information associated to each collected seed, which started to include the name of the species, subspecies, variety or form of the plants, taxonomic authority, as well as the exact collection date and site. By 1932, the Botanic Garden was regularly exchanging seeds with 359 institutions worldwide, and at its peak, the service offered seeds of 2,758 species, shipping over 11,000 seed packages to 800 scientific institutions around the globe37,38.
Methods
Our dataset includes the records collected since 1926 by the staff of the Botanic Garden of the University of Coimbra that include the date, location, and species or infraspecific taxa for the seeds collected every year to integrate the seed exchange catalogue. These records were stored in a wood cabinet (“armário” in Portuguese) and kept in the original handwritten cards, to which every year a new location and date was added when each taxon was newly collected (Fig. 1). The dataset includes both native and introduced species, as well as spontaneous and cultivated species collected inside the Botanic Garden, but also on dedicated field trips across continental Portugal, including the Berlengas island (Fig. 2). The initial dataset included 138,191 entries, which were carefully curated and georeferenced, resulting in 127,747 fully validated records after discarding incomplete, dubious or duplicated records, as well as those referring to reproductive organs other than seeds (i.e. bulbs and fern spores). Finally, a small proportion of the most recent records (2.7%) were retrieved directly from field notebooks that had not been incorporated into the cards catalogue, and an additional 0.9% were retrieved from the online catalogue of the Herbarium of the University of Coimbra, where they have been directly entered (https://coicatalogue.uc.pt, accessed on 2023-01-05). The complete dataset includes collection records for 4,462 plant taxa.
The day of collection indicates that at least one individual plant of that taxon was fruiting on a given day, at a given site. Since the collected seeds were destined to germplasm exchange programs, collectors specifically targeted ripe fruits with viable seeds. This means that seeds that were not fully formed and likely to be viable (based on the accumulated experience of the collectors/gardeners for each plant species) would not be collected and that site would need to be revisited latter to collect ripe fruits.
Taxonomic harmonization
Botanical nomenclature was first manually verified by in-house botanists that uniformized small spelling mistakes and confirmed the taxonomic authorities. This consolidated list was then harmonized with the Global Names Resolver with function gnr_resolve() in R39, with the package taxize 0.9.940,41, against the Global Biodiversity Information Facility (GBIF) backbone taxonomy accessed on 2023-03-01. The accepted taxon name and taxonomic rank were extracted at this stage (Table 1).
Table 1.
Term | Description |
---|---|
catalogNumber | Unique record number within dataset |
occurrenceID | Persistent global unique identifier number, generated by https://guidgenerator.com/ |
otherCatalogNumbers | Number of the drawer and card (in the example: Drawer 15, card 314; see also Fig. 1b) |
basisOfRecord | Type of data recording method |
year | Year of collection |
month | Month of collection |
day | Day of collection |
eventDate | Date of collection in the format yyyy-mm-dd |
dynamicProperties | Complete name and authority of the taxon accepted in WCVP42. Formatted in JSON. |
scientificName | Complete name and authority of the taxon accepted in GBIF50. |
class | Taxonomic class of the taxon (GBIF) |
order | Taxonomic order of the taxon (GBIF) |
family | Taxonomic family of the taxon (GBIF) |
genus | Taxonomic genus of the taxon (GBIF) |
establishmentMeans | Native or Introduced taxon in Portugal, according to the WCVP |
verbatimIdentification | Original taxon used in automated homogenization following curation by in-house botanists |
locality | Lowest unified toponymy of the collection site |
decimalLatitude | Latitude (in decimal degree) of the site where the plant was fruiting |
decimalLongitude | Longitude (in decimal degree) of the site where the plant was fruiting |
coordinateUncertaintyInMeters | Coordinate uncertainty in meters |
minimumElevationInMeters | Elevation (m) above sea level, obtained with the Google Elevation API from coordinates |
continent | Continent of the collection site |
country | Country of the collection site |
stateProvince | First order administrative region (”Distritos”), equivalent to states or provinces, from Google Geocoding API |
municipality | Second order administrative region (“Concelhos”) equivalent to municipalities, obtained by Google Geocoding API |
locationRemarks | Whether the seeds were collected inside or outside the Botanic Garden |
verbatimLocality | Original location name written on the card with a minimum level of curation |
georeferencedBy | Person responsible for georeferencing the collection site and associated uncertainty |
geodeticDatum | Geodetic datum upon which the geographic coordinates are based |
georeferenceProtocol | Manual used to determine the geographic coordinates and uncertainties |
link_radius_map(only available on figshare) | Direct link for the unified location of each collection locality. |
Binomial (only available on figshare) | Name of the accepted Genus and specific epithet of each record without the authority. This is not a Darwin Core field, but it’s useful for most common data manipulations |
licence | Licence associated with the record |
The list of native species for Portugal was extracted from the World Checklist of Vascular Plants (WCVP42) with function wcvp_distribution() in the R package rWCVP 1.2.443 accessed on 2023-06-28. Species that were collected in the country but are not considered native were classified as introduced. To facilitate data interoperability, the dataset includes the original name, as well as the harmonized taxonomy according to both GBIF and the WCVP.
Georeferencing protocol
Throughout the 87 years of data collection, the same collection site was often recorded with slightly different wording by different generations of collectors. The original list of localities, containing 3,753 distinct entries, was initially clustered based on the textual description using OpenRefine and then manually confirmed and further grouped into 1,485 unique curated localities. This clustering was performed only on toponymical homogenization without any loss of spatial accuracy (i.e., all unique sites were preserved and not clustered into broader categories). The final list of localities was georeferenced using the point-radius georeferencing method44,45. The latitude and longitude of each point and the confidence level for each coordinate was obtained using the online tool available on Maps.ie46 and coordinate uncertainty was calculated according to the Georeferencing Calculator47,48. The administrative levels below country (stateProvince and municipality) were obtained from the Google Geocoding API49 by submitting the latitude and longitude coordinates to the Reverse Geocoding Service. The estimated altitude for each pair of coordinates (minimumElevationInMeters) was obtained using the Google Elevation API.
Data Records
The dataset is available at GBIF50 as a species occurrences map, and can also be downloaded from figshare51 as a single text file with information on 127,747 records arranged along 33 columns (total file size 89MB). Table headings follow the Darwin Core guidelines52.
Technical Validation
The work largely benefited from the experience of Arménio Matos, Agostinho Salgado, and António Coutinho who actively participated in field sampling campaigns since 1972 and were thus familiarized with the collection protocols, species, and collection sites. The accumulated knowledge of the Herbarium of the University of Coimbra (COI) staff, namely Filipe Covelo, Joaquim Santos, and Fátima Sales, was also invaluable in curating the dataset, as many seeds were collected from the same populations (and often collected simultaneously from the same individuals) from where herbarium specimens were also collected.
Final quality check
Intermediate quality checks were routinely performed during data entry, taxonomic harmonization and georeferencing to detect and correct errors. Lastly, when the dataset was completed, we performed a new and standardized quality check to evaluate the accuracy of the data. For this, we randomly selected 1,000 records using a random number generator and carefully rechecked all the information against the original cards. We found data transcription errors on 7 records that resulted in errors on the collection day (n = 3 records), month (n = 3 records), and taxa (n = 1 record), corresponding to an overall error rate of 0.7%.
Usage Notes
The names provided in the fields “ScientificName” have already been harmonized according to the GBIF Backbone Taxonomy (see Taxonomic harmonization above). Therefore, for future taxonomical clarifications, users should use the “verbetimIdentification” field which corresponds to the original taxonomic treatment with only minor in-house manual corrections. To facilitate data interoperability, species names according to the WCVP is also provided in the subfield “scientificName_WCVP” in “dynamicProperties .
Acknowledgements
The digitalization and curation of this dataset was funded by the Portuguese Foundation for Science and Technology (FCT) through project LIFE AFTER FIRE 10.54499/PTDC/BIA-ECO/1983/2020, and grants 10.54499/UIDB/04004/2020, 10.54499/LA/P/0092/2020, 10.54499/CEECIND/00135/2017, 10.54499/CEECINST/00152/2018/CP1570/CT0014, 10.54499/2019.144414.BD and 10.54499/2020.07175.BD.
Author contributions
R.H., S.T., J.M.C., P.L., J.S., A.C.G. and F.C. designed the study and coordinated data acquisition, processing, and writing. A.M., A.S. and A.C. participated in the field sampling campaigns between 1972 and 2013. All authors actively contributed to collect, insert, interpret, or curate the data, and approved the final manuscript.
Code availability
The following code can be used to import the dataset into R and to produce basic descriptive plots at the general and specific levels (Fig. 3). Since some taxonomic authorities (i.e. the name of the taxon author) include apostrophes, such as Tetragonia crystallina L’Hér., to import data correctly, it might be necessary to specify that these are not quotes (with, quote = "\"",).
data < - read.csv("~path/data.csv", quote = "\"", sep = ";")
#Number of unique species collected per year (Fig. 3a) barplot (rowSums(table(data$year, data$scientificName) >0))
# Number of records on the entire dataset per month (Fig. 3b) barplot (table(data$month))
# Number of records per month for a single species (Fig. 3c) with(subset(data, scientificName == "Drosophyllum lusitanicum (L.) Link"),barplot(table(factor(month, levels = 1:12)), xlim = c(1, 12))).
Competing interests
The authors declare no competing interests.
Footnotes
Publisher’s note Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.
References
- 1.Menzel A, et al. European phenological response to climate change matches the warming pattern. Global change biology. 2006;12:1969–1976. doi: 10.1111/j.1365-2486.2006.01193.x. [DOI] [Google Scholar]
- 2.Zimova M, Willard DE, Winger BM, Weeks BC. Widespread shifts in bird migration phenology are decoupled from parallel shifts in morphology. J. Anim. Ecol. 2021;90:2348–2361. doi: 10.1111/1365-2656.13543. [DOI] [PubMed] [Google Scholar]
- 3.Macgregor CJ, et al. Climate-induced phenology shifts linked to range expansions in species with multiple reproductive cycles per year. Nature Communications. 2019;10:4455. doi: 10.1038/s41467-019-12479-w. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 4.Peñuelas J, Filella I. Responses to a warming world. Science. 2001;294:793–795. doi: 10.1126/science.1066860. [DOI] [PubMed] [Google Scholar]
- 5.Root TL, et al. Fingerprints of global warming on wild animals and plants. Nature. 2003;421:57–60. doi: 10.1038/nature01333. [DOI] [PubMed] [Google Scholar]
- 6.Calinger KM, Queenborough S, Curtis PS. Herbarium specimens reveal the footprint of climate change on flowering trends across north‐central North America. Ecol. Lett. 2013;16:1037–1044. doi: 10.1111/ele.12135. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 7.Fitter A, Fitter R. Rapid changes in flowering time in British plants. Science. 2002;296:1689–1691. doi: 10.1126/science.1071617. [DOI] [PubMed] [Google Scholar]
- 8.Willems, F. M., Scheepens, J. F. & Bossdorf, O. Forest wildflowers bloom earlier as Europe warms: lessons from herbaria and spatial modelling. New Phytol. 10.1111/nph.18124 (2022). [DOI] [PubMed]
- 9.Traveset, A., Heleno, R. H. & Nogales, M. in Seeds: The ecology of regeneration in plant communities (ed R. S. Gallagher) Ch. 3, 62–93 (CABI, 2014).
- 10.Murdoch, A. in Seeds: The ecology of regeneration in plant communities (ed R. S. Gallagher) Ch. 7, 151–177 (CABI, 2014).
- 11.Sherry RA, et al. Divergence of reproductive phenology under climate warming. Proceedings of the National Academy of Sciences. 2007;104:198–202. doi: 10.1073/pnas.0605642104. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 12.Ting S, Hartley S, Burns K. Global patterns in fruiting seasons. Glob. Ecol. Biogeogr. 2008;17:648–657. doi: 10.1111/j.1466-8238.2008.00408.x. [DOI] [Google Scholar]
- 13.Oberrath R, Böhning-Gaese K. Phenological adaptation of ant‐dispersed plants to seasonal variation in ant activity. Ecology. 2002;83:1412–1420. doi: 10.1890/0012-9658(2002)083[1412:PAOADP]2.0.CO;2. [DOI] [Google Scholar]
- 14.Du Y, et al. Macro‐scale variation and environmental predictors of flowering and fruiting phenology in the Chinese angiosperm flora. J. Biogeogr. 2020;47:2303–2314. doi: 10.1111/jbi.13938. [DOI] [Google Scholar]
- 15.Mendes, S. B., Olesen, J. M., Timóteo, S. & Heleno, R. Fruiting phenology matters. Plants, People, Planet (2023).
- 16.Morellato LPC, et al. Linking plant phenology to conservation biology. Biol. Conserv. 2016;195:60–72. doi: 10.1016/j.biocon.2015.12.033. [DOI] [Google Scholar]
- 17.Costa JM, et al. Species temporal persistence promotes the stability of fruit-frugivore interactions across a five-year multilayer network. J. Ecol. 2020 doi: 10.1111/1365-2745.13391. [DOI] [Google Scholar]
- 18.González-Varo JP, et al. Limited potential for bird migration to disperse plants to cooler latitudes. Nature. 2021;595:75–79. doi: 10.1038/s41586-021-03665-2. [DOI] [PubMed] [Google Scholar]
- 19.Costa A, et al. Seasonal variation in impact of non‐native species on tropical seed dispersal networks. Funct. Ecol. 2022;36:2713–2726. doi: 10.1111/1365-2435.14171. [DOI] [Google Scholar]
- 20.Heleno, R. in Plant Invasions: the role of biotic interactions (eds A. Traveset & D. Richardson) 256–269 (CABI, 2020).
- 21.Miller RG, et al. Mechanisms of fire seasonality effects on plant populations. Trends Ecol. Evol. 2019;34:1104–1117. doi: 10.1016/j.tree.2019.07.009. [DOI] [PubMed] [Google Scholar]
- 22.Keith DA, Dunker B, Driscoll DA. Dispersal: the eighth fire seasonality effect on plants. Trends Ecol. Evol. 2020;35:305–307. doi: 10.1016/j.tree.2019.12.001. [DOI] [PubMed] [Google Scholar]
- 23.Gallinat AS, Russo L, Melaas EK, Willis CG, Primack RB. Herbarium specimens show patterns of fruiting phenology in native and invasive plant species across New England. Am. J. Bot. 2018;105:31–41. doi: 10.1002/ajb2.1005. [DOI] [PubMed] [Google Scholar]
- 24.Ihne, E. & Hoffmann, H. Beiträge zur Phänologie: Geschichte der pflanzenphänologischen Beobachtungen in Europa nebst Verzeichnis der Schriften, in welchen sie niedergelegt sind. (J Rickersche Buchh, 1884).
- 25.Stevenson PR, Vargas IN. Sample size and appropriate design of fruit and seed traps in tropical forests. J. Trop. Ecol. 2008;24:95–105. doi: 10.1017/S0266467407004646. [DOI] [Google Scholar]
- 26.Willis CG, et al. Old plants, new tricks: Phenological research using herbarium specimens. Trends Ecol. Evol. 2017;32:531–546. doi: 10.1016/j.tree.2017.03.015. [DOI] [PubMed] [Google Scholar]
- 27.Hudson, I. L. & Keatley, M. R. Phenological research. Methods for environmental and climate change analysis, 177–208 (2010).
- 28.Belitz MW, Larsen EA, Shirey V, Li D, Guralnick RP. Phenological research based on natural history collections: Practical guidelines and a lepidopteran case study. Funct. Ecol. 2023;37:234–247. doi: 10.1111/1365-2435.14173. [DOI] [Google Scholar]
- 29.Yost JM, et al. Digitization protocol for scoring reproductive phenology from herbarium specimens of seed plants. Applications in Plant Sciences. 2018;6:e1022. doi: 10.1002/aps3.1022. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 30.Mendoza I, Peres CA, Morellato LPC. Continental-scale patterns and climatic drivers of fruiting phenology: A quantitative Neotropical review. Global and Planetary Change. 2017;148:227–241. doi: 10.1016/j.gloplacha.2016.12.001. [DOI] [Google Scholar]
- 31.Morellato, L. P. C. et al. The influence of sampling method, sample size, and frequency of observations on plant phenological patterns and interpretation in tropical forest trees. (Springer, 2010).
- 32.Chuine I, et al. Grape ripening as a past climate indicator. Nature. 2004;432:289–290. doi: 10.1038/432289a. [DOI] [PubMed] [Google Scholar]
- 33.Croat, T. B. Phenological behavior of habit and habitat classes on Barro Colorado Island (Panama Canal Zone). Biotropica, 270–277 (1975).
- 34.Kümmel F. Pflanzen-und Samenverzeichnisse des Botanischen Gartens der Universität Halle seit 1749. Schlechtendalia. 2010;20:57–78. [Google Scholar]
- 35.Havinga R, et al. The Index Seminum: Seeds of change for seed exchange. Taxon. 2016;65:333–336. doi: 10.12705/652.9. [DOI] [Google Scholar]
- 36.Carrisso, L. W. Notice sur le service d'échange de graines. (Imprensa da Universidade de Coimbra, 1932).
- 37.Reis, C. S., Gonçalves, L., Azevedo, C. & Trincão, P. No Jardim há histórias sem fim. (Imprensa da Universidade de Coimbra, 2014).
- 38.Silva, A. M. D. D. O sistema de informação Jardim Botânico da Universidade de Coimbra: perspetiva sistémica e visão holística da informação PhD thesis, Universidade de Coimbra, (2021).
- 39.R Development Core Team. R: A language and environment for statistical computing. (2023).
- 40.Chamberlain, S. & Szöcs, E. taxize: taxonomic search and retrieval in R. (2013). [DOI] [PMC free article] [PubMed]
- 41.Chamberlain, S. et al. taxize: Taxonomic information from around the web. R package version 0.992 (2020).
- 42.Govaerts R, Nic Lughadha E, Black N, Turner R, Paton A. The World Checklist of Vascular Plants, a continuously updated resource for exploring global plant diversity. Scientific Data. 2021;8:215. doi: 10.1038/s41597-021-00997-6. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 43.Brown, M. J. et al. rWCVP: a companion R package for the World Checklist of Vascular Plants. New Phytol. (2023). [DOI] [PubMed]
- 44.Chapman, A. D. & Wieczorek, J. R. Georeferencing best practices. Version 1.0. (2020).
- 45.Zermoglio, P., Chapman, A., Wieczorek, J., Luna, M. & Bloom, D. Georeferencing Quick Reference Guide. (GBIF Secretariat, Copenhagen, 2020).
- 46.Maps.ie. https://www.maps.ie/draw-radius-circle-map. accessed on 2023-03-20, 2023).
- 47.Bloom, D. A., Wieczorek, J. R. & Zermoglio, P. F. Georeferencing Calculator Manual. Version 1.0. (2020).
- 48.Wieczorek, C. & Wieczorek, J. Georeferencing Calculator; http://georeferencing.org/georefcalculator/gc.html. accessed on 2022-08-29, 2021).
- 49.Google. Google Geocoding APIhttps://developers.google.com/maps/documentation/geocoding/start. accessed on 2022-08-29, 2022).
- 50.Heleno R, 2024. O armário: Fruiting phenology data for 4,462 plant taxa in Portugal (1926–2013) version 1.1. GBIF. [DOI] [PMC free article] [PubMed]
- 51.Heleno R, 2024. Supporting data for “O armário: Fruiting phenology data for 4,462 plant taxa in Portugal (1926–2013)”. figshare. [DOI] [PMC free article] [PubMed]
- 52.Darwin Core Maintenance Group. Darwin Core Quick Reference, GuideBiodiversity Information Standards (TDWG). https://dwc.tdwg.org/terms/. (2021).
Associated Data
This section collects any data citations, data availability statements, or supplementary materials included in this article.
Data Citations
- Heleno R, 2024. O armário: Fruiting phenology data for 4,462 plant taxa in Portugal (1926–2013) version 1.1. GBIF. [DOI] [PMC free article] [PubMed]
- Heleno R, 2024. Supporting data for “O armário: Fruiting phenology data for 4,462 plant taxa in Portugal (1926–2013)”. figshare. [DOI] [PMC free article] [PubMed]
Data Availability Statement
The following code can be used to import the dataset into R and to produce basic descriptive plots at the general and specific levels (Fig. 3). Since some taxonomic authorities (i.e. the name of the taxon author) include apostrophes, such as Tetragonia crystallina L’Hér., to import data correctly, it might be necessary to specify that these are not quotes (with, quote = "\"",).
data < - read.csv("~path/data.csv", quote = "\"", sep = ";")
#Number of unique species collected per year (Fig. 3a) barplot (rowSums(table(data$year, data$scientificName) >0))
# Number of records on the entire dataset per month (Fig. 3b) barplot (table(data$month))
# Number of records per month for a single species (Fig. 3c) with(subset(data, scientificName == "Drosophyllum lusitanicum (L.) Link"),barplot(table(factor(month, levels = 1:12)), xlim = c(1, 12))).