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133 results for “Cactus”
Santa Rita Experimental Range site, station Santa Rita Experimental Range burned treatment: pasture 21, study of plant cover of Opuntia engelmannii (cactus apple) in units of percent on a yearly timescale
The EcoTrends project was established in 2004 by Dr. Debra Peters (Jornada Basin LTER, USDA-ARS Jornada Experimental Range) and Dr. Ariel Lugo (Luquillo LTER, USDA-FS Luquillo Experimental Forest) to support the collection and analysis of long-term ecological datasets. The project is a large synthesis effort focused on improving the accessibility and use of long-term data. At present, there are ~50 state and federally funded research sites that are participating and contributing to the EcoTrends project, including all 26 Long-Term Ecological Research (LTER) sites and sites funded by the USDA Agriculture Research Service (ARS), USDA Forest Service, US Department of Energy, US Geological Survey (USGS) and numerous universities. Data from the EcoTrends project are available through an exploratory web portal (http://www.ecotrends.info). This web portal enables the continuation of data compilation and accessibility by users through an interactive web application. Ongoing data compilation is updated through both manual and automatic processing as part of the LTER Provenance Aware Synthesis Tracking Architecture (PASTA). The web portal is a collaboration between the Jornada LTER and the LTER Network Office. The following dataset from Santa Rita Experimental Range (SRE) contains plant cover of Opuntia engelmannii (cactus apple) measurements in percent units and were aggregated to a yearly timescale.
Santa Rita Experimental Range site, station Santa Rita Experimental Range control treatment: pastures 8 and 22, study of plant cover of Opuntia engelmannii (cactus apple) in units of percent on a yearly timescale
The EcoTrends project was established in 2004 by Dr. Debra Peters (Jornada Basin LTER, USDA-ARS Jornada Experimental Range) and Dr. Ariel Lugo (Luquillo LTER, USDA-FS Luquillo Experimental Forest) to support the collection and analysis of long-term ecological datasets. The project is a large synthesis effort focused on improving the accessibility and use of long-term data. At present, there are ~50 state and federally funded research sites that are participating and contributing to the EcoTrends project, including all 26 Long-Term Ecological Research (LTER) sites and sites funded by the USDA Agriculture Research Service (ARS), USDA Forest Service, US Department of Energy, US Geological Survey (USGS) and numerous universities. Data from the EcoTrends project are available through an exploratory web portal (http://www.ecotrends.info). This web portal enables the continuation of data compilation and accessibility by users through an interactive web application. Ongoing data compilation is updated through both manual and automatic processing as part of the LTER Provenance Aware Synthesis Tracking Architecture (PASTA). The web portal is a collaboration between the Jornada LTER and the LTER Network Office. The following dataset from Santa Rita Experimental Range (SRE) contains plant cover of Opuntia engelmannii (cactus apple) measurements in percent units and were aggregated to a yearly timescale.
Santa Rita Experimental Range site, station Santa Rita Experimental Range pastures that were grazed and burned: pastures 2N and 6A, study of plant cover of Opuntia engelmannii (cactus apple) in units of percent on a yearly timescale
The EcoTrends project was established in 2004 by Dr. Debra Peters (Jornada Basin LTER, USDA-ARS Jornada Experimental Range) and Dr. Ariel Lugo (Luquillo LTER, USDA-FS Luquillo Experimental Forest) to support the collection and analysis of long-term ecological datasets. The project is a large synthesis effort focused on improving the accessibility and use of long-term data. At present, there are ~50 state and federally funded research sites that are participating and contributing to the EcoTrends project, including all 26 Long-Term Ecological Research (LTER) sites and sites funded by the USDA Agriculture Research Service (ARS), USDA Forest Service, US Department of Energy, US Geological Survey (USGS) and numerous universities. Data from the EcoTrends project are available through an exploratory web portal (http://www.ecotrends.info). This web portal enables the continuation of data compilation and accessibility by users through an interactive web application. Ongoing data compilation is updated through both manual and automatic processing as part of the LTER Provenance Aware Synthesis Tracking Architecture (PASTA). The web portal is a collaboration between the Jornada LTER and the LTER Network Office. The following dataset from Santa Rita Experimental Range (SRE) contains plant cover of Opuntia engelmannii (cactus apple) measurements in percent units and were aggregated to a yearly timescale.
Santa Rita Experimental Range site, station Santa Rita Experimental Range pastures where the mesquite were killed and the pastures were burned: pasture 2S, study of plant cover of Opuntia engelmannii (cactus apple) in units of percent on a yearly timescale
The EcoTrends project was established in 2004 by Dr. Debra Peters (Jornada Basin LTER, USDA-ARS Jornada Experimental Range) and Dr. Ariel Lugo (Luquillo LTER, USDA-FS Luquillo Experimental Forest) to support the collection and analysis of long-term ecological datasets. The project is a large synthesis effort focused on improving the accessibility and use of long-term data. At present, there are ~50 state and federally funded research sites that are participating and contributing to the EcoTrends project, including all 26 Long-Term Ecological Research (LTER) sites and sites funded by the USDA Agriculture Research Service (ARS), USDA Forest Service, US Department of Energy, US Geological Survey (USGS) and numerous universities. Data from the EcoTrends project are available through an exploratory web portal (http://www.ecotrends.info). This web portal enables the continuation of data compilation and accessibility by users through an interactive web application. Ongoing data compilation is updated through both manual and automatic processing as part of the LTER Provenance Aware Synthesis Tracking Architecture (PASTA). The web portal is a collaboration between the Jornada LTER and the LTER Network Office. The following dataset from Santa Rita Experimental Range (SRE) contains plant cover of Opuntia engelmannii (cactus apple) measurements in percent units and were aggregated to a yearly timescale.
Santa Rita Experimental Range site, station Santa Rita Experimental Range pastures where the existing mesquite were killed and the pastures were grazed: pastures 3, 5N, 5S, 6B and 12B, study of plant cover of Echinocereus (hedgehog cactus) in units of percent on a yearly timescale
The EcoTrends project was established in 2004 by Dr. Debra Peters (Jornada Basin LTER, USDA-ARS Jornada Experimental Range) and Dr. Ariel Lugo (Luquillo LTER, USDA-FS Luquillo Experimental Forest) to support the collection and analysis of long-term ecological datasets. The project is a large synthesis effort focused on improving the accessibility and use of long-term data. At present, there are ~50 state and federally funded research sites that are participating and contributing to the EcoTrends project, including all 26 Long-Term Ecological Research (LTER) sites and sites funded by the USDA Agriculture Research Service (ARS), USDA Forest Service, US Department of Energy, US Geological Survey (USGS) and numerous universities. Data from the EcoTrends project are available through an exploratory web portal (http://www.ecotrends.info). This web portal enables the continuation of data compilation and accessibility by users through an interactive web application. Ongoing data compilation is updated through both manual and automatic processing as part of the LTER Provenance Aware Synthesis Tracking Architecture (PASTA). The web portal is a collaboration between the Jornada LTER and the LTER Network Office. The following dataset from Santa Rita Experimental Range (SRE) contains plant cover of Echinocereus (hedgehog cactus) measurements in percent units and were aggregated to a yearly timescale.
Santa Rita Experimental Range site, station Santa Rita Experimental Range pastures where the existing mesquite were killed and the pastures were grazed: pastures 3, 5N, 5S, 6B and 12B, study of plant cover of Mammillaria (globe cactus) in units of percent on a yearly timescale
The EcoTrends project was established in 2004 by Dr. Debra Peters (Jornada Basin LTER, USDA-ARS Jornada Experimental Range) and Dr. Ariel Lugo (Luquillo LTER, USDA-FS Luquillo Experimental Forest) to support the collection and analysis of long-term ecological datasets. The project is a large synthesis effort focused on improving the accessibility and use of long-term data. At present, there are ~50 state and federally funded research sites that are participating and contributing to the EcoTrends project, including all 26 Long-Term Ecological Research (LTER) sites and sites funded by the USDA Agriculture Research Service (ARS), USDA Forest Service, US Department of Energy, US Geological Survey (USGS) and numerous universities. Data from the EcoTrends project are available through an exploratory web portal (http://www.ecotrends.info). This web portal enables the continuation of data compilation and accessibility by users through an interactive web application. Ongoing data compilation is updated through both manual and automatic processing as part of the LTER Provenance Aware Synthesis Tracking Architecture (PASTA). The web portal is a collaboration between the Jornada LTER and the LTER Network Office. The following dataset from Santa Rita Experimental Range (SRE) contains plant cover of Mammillaria (globe cactus) measurements in percent units and were aggregated to a yearly timescale.
Santa Rita Experimental Range site, station Santa Rita Experimental Range pastures where the existing mesquite were killed and the pastures were grazed: pastures 3, 5N, 5S, 6B and 12B, study of plant cover of Opuntia engelmannii (cactus apple) in units of percent on a yearly timescale
The EcoTrends project was established in 2004 by Dr. Debra Peters (Jornada Basin LTER, USDA-ARS Jornada Experimental Range) and Dr. Ariel Lugo (Luquillo LTER, USDA-FS Luquillo Experimental Forest) to support the collection and analysis of long-term ecological datasets. The project is a large synthesis effort focused on improving the accessibility and use of long-term data. At present, there are ~50 state and federally funded research sites that are participating and contributing to the EcoTrends project, including all 26 Long-Term Ecological Research (LTER) sites and sites funded by the USDA Agriculture Research Service (ARS), USDA Forest Service, US Department of Energy, US Geological Survey (USGS) and numerous universities. Data from the EcoTrends project are available through an exploratory web portal (http://www.ecotrends.info). This web portal enables the continuation of data compilation and accessibility by users through an interactive web application. Ongoing data compilation is updated through both manual and automatic processing as part of the LTER Provenance Aware Synthesis Tracking Architecture (PASTA). The web portal is a collaboration between the Jornada LTER and the LTER Network Office. The following dataset from Santa Rita Experimental Range (SRE) contains plant cover of Opuntia engelmannii (cactus apple) measurements in percent units and were aggregated to a yearly timescale.
Data from: Saguaro (Carnegiea gigantea) mortality and population regeneration in the cactus forest of Saguaro National Park: seventy-five years and counting
Annual census data spanning seventy-five years document mortality and regeneration in a population of saguaro cactus (Carnegiea gigantea) in the Cactus Forest of the Rincon Mountain District of Saguaro National Park near Tucson, AZ. On 6 four-hectare plots, each saguaro was censused and a methodical search for new saguaros was conducted annually each year from 1942 through 2016, with the exception of 1955. Regeneration has been episodic with 828 plants established from 1959 through 1993 compared with 34 plants established between 1942 and 1958 and only three plants established after 1993. The years preceding 1959 and following 1993, include some of the driest decades in centuries in southern Arizona. While woodcutting and cattle grazing are believed to be among the causes of decades of failed regeneration prior to 1958, neither of these factors contributed to the failed regeneration following 1993. The height structure of the population from 1942 to 2016 shifted dramatically from a population dominated by large saguaros (> 5.4 m tall) in the first three decades of the study to a population dominated by small saguaros (< 1.8 m tall) in the most recent two decades. Mortality is shown to be strongly age dependent. In the year following the 2011 catastrophic freeze, 21 of 59 plants older than 80 years died compared with zero deaths in 270 plants between the ages of 29 and 80 years. Saguaros under 40 years old, growing under small shrubs or in the open, have a lower probability of survival than better protected saguaros. Long-term population monitoring is essential to understanding the complex impacts of human and environmental factors on the population dynamics of long-lived species.
Data from: Interglacial microrefugia and diversification of a cactus species complex: phylogeography and palaeodistributional reconstructions for Pilosocereus aurisetus and allies
The role of Pleistocene climate changes in promoting evolutionary diversification in global biota is well documented, but the great majority of data regarding this subject come from North America and Europe, which were greatly affected by glaciation. The effects of Pleistocene changes on cold- and/or dry-adapted species in tropical areas where glaciers were not present remain sparsely investigated. Many such species are restricted to small areas surrounded by unfavourable habitats, which may represent potential interglacial microrefugia. Here, we analysed the phylogeographic structure and diversification history of seven cactus species in the Pilosocereus aurisetus complex that are restricted to rocky areas with high diversity and endemism within the Neotropical savannas of eastern South America. We combined palaeodistributional estimates with standard phylogeographic approaches based on two chloroplast DNA regions (trnT-trnL and trnS-trnG), exon 1 of the nuclear gene PhyC and 10 nuclear microsatellite loci. Our analyses revealed a phylogeographic history marked by multiple levels of distributional fragmentation, isolation leading to allopatric differentiation and secondary contact among divergent lineages within the complex. Diversification and demographic events appear to have been affected by the Quaternary climatic cycles as a result of isolation in multiple patches of xerophytic vegetation. These small patches presently harbouring P. aurisetus populations seem to operate as microrefugia, both at present and during Pleistocene interglacial periods; the role of such microrefugia should be explored and analysed in greater detail.
Data from: Influence of Pleistocene glacial/interglacial cycles on the genetic structure of the mistletoe cactus Rhipsalis baccifera (Cactaceae) in Mesoamerica
Phylogeographical work on cloud forest-adapted species provides inconsistent evidence on cloud forest dynamics during glacial cycles. A study of Rhipsalis baccifera (Cactaceae), a bird-dispersed epiphytic mistletoe cactus, was conducted to investigate genetic variation at sequence data from nuclear [internal transcribed spacer (ITS), 677 bp] and chloroplast (rpl32-trnL, 1092bp) DNA for 154 individuals across the species range in Mesoamerica to determine if such patterns are consistent with the expansion/contraction model of cloud forest during glacial cycles. We conducted population and spatial genetic analyses as well as gene flow and divergence time estimates between 24 populations comprising the distribution of R. baccifera in Mexico and Guatemala to gain insight of the evolutionary history of these populations, and a complementary species distribution modeling approach to frame information derived from the genetic analyses into an explicit paleoecological context. The results revealed a phylogeographical break at the Isthmus of Tehuantepec, and high levels of genetic diversity among populations and cloud forest areas. Despite the genetic differentiation of some R. baccifera populations, the widespread ITS ribotypes suggest effective nuclear gene flow via pollen and population differentiation shown by the rpl32-trnL suggests more restricted seed flow. Predictions of species distribution models under past last glacial maximum (LGM) climatic conditions and a significant signal of demographic expansion suggest that R. baccifera populations experienced a range expansion tracking the conditions of the cloud forest distribution and shifted to the lowlands with population connectivity during the LGM.
Data from: Model-based analysis supports interglacial refugia over long-dispersal events in the diversification of two South American cactus species
Pilosocereus machrisii and P. aurisetus are cactus species within the P. aurisetus complex, a group of eight cacti that are restricted to rocky habitats within the Neotropical savannas of eastern South America. Previous studies have suggested that diversification within this complex was driven by distributional fragmentation, isolation leading to allopatric differentiation, and secondary contact among divergent lineages. These events have been associated with Quaternary climatic cycles, leading to the hypothesis that the xerophytic vegetation patches which presently harbor these populations operate as refugia during the current interglacial. However, owing to limitations of the standard phylogeographic approaches used in these studies, this hypothesis was not explicitly tested. Here we use Approximate Bayesian Computation to refine the previous inferences and test the role of different events in the diversification of two species within P. aurisetus group. We used molecular data from chloroplast DNA and simple sequence repeats loci of P. machrisii and P. aurisetus, the two species with broadest distribution in the complex, in order to test if the diversification in each species was driven mostly by vicariance or by long-dispersal events. We found that both species were affected primarily by vicariance, with a refuge model as the most likely scenario for P. aurisetus and a soft vicariance scenario most probable for P. machrisii. These results emphasize the importance of distributional fragmentation in these species, and add support to the hypothesis of long-term isolation in interglacial refugia previously proposed for the P. aurisetus species complex diversification.
Fig. 2 in Current and Potential Distribution of the Cactus Weevil,Cactophagus spinolae(Gyllenhal) (Coleoptera: Curculionidae), in Mexico
Fig. 2. Distribution of five commercial Cactaceae commodities in Mexico. A) Prickly pear pad, B) Opuntia fodder, C) Prickly pear fruit, D) Dragon fruit, E) Pitahaya.
Fig. 1 in Current and Potential Distribution of the Cactus Weevil,Cactophagus spinolae(Gyllenhal) (Coleoptera: Curculionidae), in Mexico
Fig. 1. Potential distribution of Cactophagus spinolae in Mexico. Biogeographic provinces (Morrone 2005, 2014a): 1 = California; 2 = Baja California; 3 = Sonora; 4 = Sierra Madre Occidental; 5 = Mexican Plateau; 6 = Tamaulipeca; 7 = Mexican Pacific Coast; 8 = Transmexican Volcanic Belt; 9 = Sierra Madre Oriental; 10 = Veracruzana; 11 = Balsas Basin; 12 = Sierra Madre del Sur; 13 = Chiapas; 14 = Yucatán. Scale values: blue = absent (0); red = present (1).
Botella Cactus
Source: Objaverse 1.0 / Sketchfab
Cactus Vase
Was so hard to make this. Lord. Source: Objaverse 1.0 / Sketchfab
On following pages: 248. Merriam''s Deermouse (Peromyscus merriami); 249. Cactus Deermouse (Peromyscus eremicus); 250. San Lorenzo Deermouse (Peromyscus interparietalis); 251. Southern Baja Deermouse (Peromyscus eva); 252. Northern Baja Deermouse (Peromyscus fraterculus); 253. Monserrat Island Deermouse (Peromyscus caniceps); 254. Dickey's Deermouse (Peromyscus dickeyi); 255. La Guarda Deermouse (Peromyscus guardia); 256. Coronados Deermouse (Peromyscus pseudocrinitus); 257. Cotton Deermouse (Peromyscus gossypinus); 258. White-footed Deermouse (Peromyscus leucopus); 259. Santa Cruz Deermouse (Peromyscus sejugis); 260. North-western Deermouse (Peromyscus keeni): 261. Oldfield Deermouse (Peromyscus polionotus); 262. North American Deermouse (Peromyscus maniculatus); 263. Black-eared Deermouse (Peromyscus melanotis); 264. Black-tailed Deermouse (Peromyscus melanurus); 265. Broad-faced Deermouse (Peromyscus megalops); 266. Black-wristed Deermouse (Peromyscus melanocarpus); 267. Catalina Deermouse (Peromyscus slevini); 268. Tawny Deermouse (Peromyscus perfulvus); 269. Plateau Deermouse (Peromyscus melanophrys); 270. Puebla Deermouse (Peromyscus mekisturus); 271. Mayan Deermouse (Peromyscus mayensis); 272. Stirton's Deermouse (Peromyscus stirtoni); 273. Yucatan Deermouse (Peromyscus yucatanicus); 274. Chimoxan Deermouse (Peromyscus tropicalis); 275. Talamancan Deermouse (Peromyscus nudipes); 276. Mexican Deermouse (Peromyscus mexicanus); 277. Naked-eared Deermouse (Peromyscus gymnotis); 278. Chiapan Deermouse (Peromyscus zarhynchus); 279. Gardner's Deermouse (Peromyscus gardneri); 280. Nicaraguan Deermouse (Peromyscus nicaraguae); 281. Salvadorean Deermouse (Peromyscus salvadorensis); 282. Guatemalan Deermouse (Peromyscus guatemalensis); 283. Large Deermouse (Peromyscus grandis). in Cricetidae
On following pages: 248. Merriam''s Deermouse (Peromyscus merriami); 249. Cactus Deermouse (Peromyscus eremicus); 250. San Lorenzo Deermouse (Peromyscus interparietalis); 251. Southern Baja Deermouse (Peromyscus eva); 252. Northern Baja Deermouse (Peromyscus fraterculus); 253. Monserrat Island Deermouse (Peromyscus caniceps); 254. Dickey's Deermouse (Peromyscus dickeyi); 255. La Guarda Deermouse (Peromyscus guardia); 256. Coronados Deermouse (Peromyscus pseudocrinitus); 257. Cotton Deermouse (Peromyscus gossypinus); 258. White-footed Deermouse (Peromyscus leucopus); 259. Santa Cruz Deermouse (Peromyscus sejugis); 260. North-western Deermouse (Peromyscus keeni): 261. Oldfield Deermouse (Peromyscus polionotus); 262. North American Deermouse (Peromyscus maniculatus); 263. Black-eared Deermouse (Peromyscus melanotis); 264. Black-tailed Deermouse (Peromyscus melanurus); 265. Broad-faced Deermouse (Peromyscus megalops); 266. Black-wristed Deermouse (Peromyscus melanocarpus); 267. Catalina Deermouse (Peromyscus slevini); 268. Tawny Deermouse (Peromyscus perfulvus); 269. Plateau Deermouse (Peromyscus melanophrys); 270. Puebla Deermouse (Peromyscus mekisturus); 271. Mayan Deermouse (Peromyscus mayensis); 272. Stirton's Deermouse (Peromyscus stirtoni); 273. Yucatan Deermouse (Peromyscus yucatanicus); 274. Chimoxan Deermouse (Peromyscus tropicalis); 275. Talamancan Deermouse (Peromyscus nudipes); 276. Mexican Deermouse (Peromyscus mexicanus); 277. Naked-eared Deermouse (Peromyscus gymnotis); 278. Chiapan Deermouse (Peromyscus zarhynchus); 279. Gardner's Deermouse (Peromyscus gardneri); 280. Nicaraguan Deermouse (Peromyscus nicaraguae); 281. Salvadorean Deermouse (Peromyscus salvadorensis); 282. Guatemalan Deermouse (Peromyscus guatemalensis); 283. Large Deermouse (Peromyscus grandis).
Data from: Habitat fragmentation in coastal southern California disrupts genetic connectivity in the Cactus Wren (Campylorhynchus brunneicapillus)
Achieving long-term persistence of species in urbanized landscapes requires characterizing population genetic structure to understand and manage the effects of anthropogenic disturbance on connectivity. Urbanization over the past century in coastal southern California has caused both precipitous loss of coastal sage scrub habitat and declines in populations of the cactus wren (Campylorhynchus brunneicapillus). Using 22 microsatellite loci, we found that remnant cactus wren aggregations in coastal southern California comprised 20 populations based on strict exact tests for population differentiation, and 12 genetic clusters with hierarchical Bayesian clustering analyses. Genetic structure patterns largely mirrored underlying habitat availability, with cluster and population boundaries coinciding with fragmentation caused primarily by urbanization. Using a habitat model we developed, we detected stronger associations between habitat-based distances and genetic distances than Euclidean geographic distance. Within populations, we detected a positive association between available local habitat and allelic richness and a negative association with relatedness. Isolation-by-distance patterns varied over the study area, which we attribute to temporal differences in anthropogenic landscape development. We also found that genetic bottleneck signals were associated with wildfire frequency. These results indicate that habitat fragmentation and alterations have reduced genetic connectivity and diversity of cactus wren populations in coastal southern California. Management efforts focused on improving connectivity among remaining populations may help to ensure population persistence.
Fig. 1 in Effect of Gerstaeckeria bifasciata (Gerstaecker, 1860) (Coleoptera: Curculionidae: Cryptorhynchinae) Herbivory on a Globose Cactus in Guanajuato, Mexico
Fig. 1. Distribution of the number of ribs damaged by Gerstaeckeria bifasciata in individuals of Stenocactus obvallatus during 2017 (N = 337). Average ± standard deviation (SD) is indicated.
Fig. 2 in Effect of Gerstaeckeria bifasciata (Gerstaecker, 1860) (Coleoptera: Curculionidae: Cryptorhynchinae) Herbivory on a Globose Cactus in Guanajuato, Mexico
Fig. 2. Damage caused by Gerstaeckeria bifasciata on Stenocactus obvallatus in Tierra Blanca, Guanajuato, Mexico. A) G. bifasciata feeding from ribs, B) Flower bud eaten by G. bifasciata.
Fig. 3. Stenocactus obvallatus. A in Effect of Gerstaeckeria bifasciata (Gerstaecker, 1860) (Coleoptera: Curculionidae: Cryptorhynchinae) Herbivory on a Globose Cactus in Guanajuato, Mexico
Fig. 3. Stenocactus obvallatus. A) Without feeding damage, B) After six months of herbivory by Gerstaeckeria bifasciata (some spines removed to better observe damage).
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Allen Brain Atlas
Allen Brain Atlas is an Allen Institute collection of brain map atlases, datasets, APIs, and analysis tools covering mouse, human, and non-human primate brain resources.
Annotated Behaviour and Observability Dataset (ABODe)
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DANDI Archive for NWB datasets
DANDI is a BRAIN Initiative archive for publishing and sharing neurophysiology data, including electrophysiology, optophysiology, and behavioral data packaged as NWB and related standards.
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.
OpenNeuro
OpenNeuro is a free, open platform for sharing neuroimaging datasets, with public search, dataset pages, and download paths for web, S3, DataLad, and the OpenNeuro CLI.