Abstract
Premise
The Campanulaceae (Lobelioideae) is the Hawaiian plant family with the most endangered and extinct species. Although seeds of Hawaiian lobelioids are desiccation tolerant, the species are exceptional (i.e., they present challenges at various stages of the conventional ex situ conservation chain) due to their generally poor seed survival at the conventional seed‐banking temperature (–18°C). Both morphological dormancy (MD) and morphophysiological dormancy (MPD) have been identified in the seeds of other Hawaiian lobelioids; however, the class of dormancy and germination requirements of the Critically Endangered genus Brighamia have not yet been determined.
Methods
We measured the embryonic growth in 12‐week‐old seeds of B. rockii and tested their germination at three temperature regimes (15/5°C, 20/10°C, and 25/15°C) in light and at 25/15°C in darkness.
Results
The embryos grew prior to radicle emergence, and the seeds germinated rapidly to high percentages in all tested conditions.
Discussion
Whether fresh B. rockii seeds have MD or MPD still needs to be determined; nevertheless, 12‐week‐old seeds germinated well in light and darkness, and thus the seeds can be used for conservation purposes. Germination in the dark suggests that the species may not form a long‐lived soil seed bank in its native habitat.
Keywords: Brighamia, critically endangered plants, embryo growth, ex situ conservation, exceptional species, Hawaiian lobelioids
Plant species are becoming extinct tens to hundreds of times faster than the background extinction rate, making the need for effective plant conservation programs more urgent than ever before (Humphreys et al., 2019; Intergovernmental Science‐Policy Platform on Biodiversity and Ecosystem Services, 2019). The Global Strategy for Plant Conservation (GSPC) provides a framework for practicing plant conservation. Target 8 of the GSPC sets the goal of conserving 75% of threatened plant species ex situ (Convention on Biological Diversity, 2011), with seed banking being the most efficient and cost‐effective means of ex situ plant conservation (Phartyal et al., 2002; Guerrant et al., 2004; Cochrane et al., 2007; Liu et al., 2018, 2020). However, not all species can be conserved using conventional seed‐banking methods (i.e., retaining long‐term viability when desiccated to a relative humidity [RH] in equilibrium with 10–25% and stored at −18°C), which is the case for endemic Hawaiian Lobelioideae (Chau et al., 2019). For seed banking to be a successful conservation strategy, seeds eventually need to be withdrawn from the seed bank and used for plant propagation; however, when the viability of seeds in the seed bank falls to an unacceptable level, additional seeds must be collected from wild plants and/or regenerated from banked seeds. Regardless of the seed source, species‐specific knowledge of dormancy‐breaking and germination requirements is needed to successfully grow plants from seeds.
The endemic Hawaiian Lobelioideae (Campanulaceae; six genera, 126 species) exemplify adaptive radiation in plants, with the Campanulaceae representing the largest family in the flora of the most isolated archipelago on Earth (Wagner et al., 2005). The lobelioid ancestor arrived in the Hawaiian Islands ca. 13 mya (Givnish et al., 2009). Eventually, species of the Lobelioideae became distributed on seven of the eight main Hawaiian Islands at elevations from <100 to >4000 m a.s.l. (Wagner et al., 1999). These plants have remarkably diverse life forms (shrubs, trees, rosettes, succulents, vines, and epiphytes) and occupy a variety of habitats (including high‐elevation bogs, cliff faces, and forests; Wagner et al., 1999). The Campanulaceae family also contains the most Hawaiian species listed under the Endangered Species Act and the highest number of recent extinctions in the state (United States Fish and Wildlife Service, 2016; Wood et al., 2019). The reason behind this high endangerment and extinction rate is uncertain; however, these plants are susceptible to destruction by rats, slugs, and diseases, and may have been impacted by the loss of specific pollinators and seed dispersers (Walsh et al., 2019; Wood et al., 2019; Rønsted et al., 2022).
While the majority of species in the Campanulaceae globally produce orthodox seeds (i.e., seeds that are desiccation and freeze tolerant and long lived; Royal Botanic Gardens Kew, 2020), this is not the case with Hawaiian‐endemic Campanulaceae, which appear to be desiccation tolerant yet lose viability faster at the conventional seed storage temperature of −18°C than at 5°C. This type of response has been termed “intermediate freeze‐sensitive storage behavior” (Chau et al., 2019).
Efforts to restore plants from seeds are often challenged by a lack of a priori knowledge of seed dormancy and germination requirements. Seeds of many species of Hawaiian Campanulaceae have morphological dormancy (MD) or morphophysiological dormancy (MPD) (Baskin et al., 2005, 2020; Baskin and Baskin, 2014). Freshly matured seeds with MD have a water‐permeable seed coat, and the embryo is small and either undifferentiated (i.e., lacking a radicle and cotyledon[s], such as members of the Orchidaceae) or differentiated (radicle and cotyledon[s] present) but underdeveloped, and must therefore grow inside the seed before radicle emergence (germination) occurs. Seeds with MD do not require dormancy‐breaking treatments per se; they merely need time for the embryo to grow and become fully developed, and can germinate in ≤1 month at favorable conditions. On the other hand, in addition to being underdeveloped, the embryo in seeds with MPD also has a physiological mechanism for germination inhibition (Baskin and Baskin, 2014). The germination of seeds with MPD is therefore delayed >1 month, and treatments such as warm and/or cold stratification are needed to break the physiological component of the embryo dormancy.
Brighamia A. Gray (Campanulaceae) is an endemic Hawaiian genus comprising two species, B. insignis A. Gray and B. rockii H. St. John (Wagner et al., 2005). Brighamia rockii (ʻolulu, alula, or puaʻalain in Hawaiian) is listed as Critically Endangered on the IUCN Red List of Threatened Species and only 11 individuals are known in the wild, all of which are located in a single subpopulation on the cliffs of Molokaʻi (Walsh et al., 2022). Seed dormancy‐break and germination have been investigated for a few species of Hawaiian Campanulaceae, and both MD and MPD have been identified (Baskin et al., 2005, 2020; Baskin and Baskin, 2014); however, the dormancy‐breaking and germination requirements have not been determined for the endemic and exceptional (i.e., presenting challenges to the conventional ex situ conservation chain) Hawaiian lobelioid genus Brighamia. Therefore, our objective in this study was to improve our understanding of the seed dormancy and germination requirements of Brighamia to inform conservation collection management. Because other lobelioids have MD or MPD, we hypothesized that the embryos in the seeds of B. rockii are underdeveloped (small) and must grow inside the seed prior to radicle emergence (germination), and therefore that the seeds have either MD or MPD.
To test our hypothesis, we asked the following questions: (i) Does the embryo length : seed length (E : S) ratio increase prior to seed germination? (ii) How quickly do seeds germinate? (iii) What are the temperature and light/dark requirements for germination? Here, we report the results of our studies, although we note that the outcome was complicated by a 12‐week storage period before our experiments began. During this time, any fully developed embryos may have transitioned from dormancy to nondormancy or, in the case of underdeveloped embryos, from MPD to MD. Despite this complication, we have gained important information about the seed germination of an endangered species.
METHODS
Seed source
Brighamia rockii occurs on the Wailau cliffs of Molokaʻi, Hawaiʻi, USA. The mean hourly temperature for this location ranges from 16.17°C (February, 07:00) to 25.02°C (September, 14:00) (Giambelluca et al., 2014). Freshly matured seeds of B. rockii were collected at the Olinda Rare Plant Facility on Maui on 30 October 2020 by Anna Palomino (Hawaiʻi Plant Extinction Prevention Program; University of Hawaiʻi Center for Conservation Research and Training; Hawaiʻi State Department of Land and Natural Resources Department of Forestry and Wildlife) from three cultivated plants (numbers 02, 03, and 09). The three plants are the progeny of a wild single maternal founder (GeoRef no. BRI‐ROC‐MO‐EHU‐A), and the seeds were pooled before shipping. Ane Bakutis (Hawaiʻi Plant Extinction Prevention Program; University of Hawaiʻi Center for Conservation Research and Training; Hawaiʻi State Department of Land and Natural Resources Department of Forestry and Wildlife) coordinated the shipment of seeds to the National Tropical Botanical Garden (NTBG), Kalāheo, Hawaiʻi. The seeds were received on 3 December 2020 and kept in paper coin envelopes in ambient lab conditions (~46% RH and 23°C) until the experiments (embryo growth and germination) were carried out, beginning on 22 January 2021.
Embryo growth
To determine whether the embryos grow inside the seeds prior to germination, the E : S ratio was determined for seeds imbibed for 24 h and for seeds when germination was imminent, i.e., at the time the seed coat had split but before the protrusion of the radicle (germination) had occurred (i.e., the maximum [critical] E : S ratio for germination). To determine the initial E : S ratio, seeds were imbibed for 24 h in 12 h light/12 h dark (hereafter, light) at 25/15°C. The seeds were then cut open lengthwise with a single‐edge razor blade and the E : S ratio was determined for 16 seeds using a micrometer in the eyepiece of a dissecting microscope. To determine the critical E : S ratio, the seeds were placed in 60‐mm Petri dishes on seed‐germination paper (Anchor Paper Company, St. Paul, Minnesota, USA) moistened with a 0.1% solution (in distilled water) of a plant preservative mixture (PPM; Plant Cell Technology, Washington, D.C., USA) to inhibit fungal growth without affecting germination (Assaf Guri, Plant Cell Technology, personal communication). The seeds were incubated in light at 25/15°C and examined every 2–3 days to identify individuals for which germination was imminent. The critical E : S ratio of five seeds was determined.
Germination
To determine the temperature and light/dark requirements for germination, three replicates of 25 seeds per germination condition were placed in 60‐mm Petri dishes on seed‐germination paper moistened with a solution of 0.1% PPM. The Petri dishes were sealed with plastic paraffin film to reduce water loss. The seeds were incubated in 12 h light/12 h dark with alternating temperature regimes of 15/5°C, 20/10°C, and 25/15°C, or in continuous darkness (Petri dishes wrapped in aluminum foil) at 25/15°C. The light was generated by fluorescent tubes, and the illuminance at the seed level was about 300 lux. Germination was monitored at two‐week (occasionally three‐week) intervals for a maximum period of 292 days. The seeds incubated in darkness were checked using a safe green light, provided by an LED with a peak wavelength at 515 nm (Feit Electric, Los Angeles, California, USA).
“Safe green lights” are commonly used to monitor the germination of dark‐incubated seeds, but green light may actually promote germination in some species, depending on the stage of dormancy break between full dormancy and nondormancy (Baskin et al., 2006). Baskin et al. (2006) suggested comparing the germination of seeds exposed to green light to that of seeds not receiving any light; therefore, we tested whether the green light promoted germination of B. rockii seeds. To achieve this, 50 seeds were placed in a 60‐mm Petri dish on seed‐germination paper moistened with a solution of 0.1% PPM. These dishes were sealed with plastic paraffin and wrapped in aluminum foil to exclude light, then incubated at 25/15°C. The dishes were not opened until the termination of the test on day 61.
We monitored the seeds (except those in continuous darkness at 25/15°C) until every seed either germinated, was conspicuously contaminated by fungi, or had been incubated for 292 days. If seeds did not resist gentle pressure from probing, they were considered to have lost viability. Germination was defined as radicle emergence, and the proportion germinated was calculated by dividing the number of seeds germinated by the number of seeds sown. Only one seed died (at 25/15°C in dark) before the experiments were terminated.
Statistical analysis
The software RStudio (RStudio Team, 2019) and environment R (R Core Team, 2021) were used for all statistical analyses, and the package ‘ggplot2’ was used for the construction of graphs (Wickham, 2016). The germination data were analyzed using a time‐to‐event model (Ritz et al., 2013) and the two‐step meta‐analytic approach described by Jensen et al. (2017, 2020), performed using the ‘drc’ package (Ritz et al., 2019). A non‐linear log‐logistic three‐parameter model was used:
where d is maximum germination, t 50 is time at which 50% of the seeds that germinated during the experiment have done so, and the absolute value b is proportional to the slope of F at time t. There were two replicates (Petri dishes) to which the model could not be fitted. In one dish at 20/10°C, the only seeds that germinated were observed at the same time, thus no parameters were estimated. In the other case, at 15/5°C, all the seeds germinated, so d (maximum germination) did not need to be estimated and was set to 1 and the model was run manually for estimates b and t 50. Jensen et al. (2017) proposed a meta‐analytic approach that allows the incorporation of the experimental design into the statistical analysis when using appropriate models at the level of the individual Petri dishes, which are treated as sub‐experiments. We used a linear mixed model in which the treatment‐by‐model parameter interaction was the only fixed effect, and the replicated Petri dishes were the random effects.
A Welch's t‐test (α = 0.05) was used to determine significant differences between the initial and critical (germination imminent) E : S ratios.
RESULTS
Embryo growth
The mean (±SE) initial embryo and seed lengths were 0.5 ± 0.02 mm and 1.1 ± 0.02 mm, respectively. At imminent germination, the embryo and seed lengths were 1.0 ± 0.04 mm and 1.1 ± 0.05 mm, respectively. The initial E : S ratio was therefore 0.49, while at imminent germination it was 0.92, representing a significant (P < 0.0001) increase of 87.8% in 12 days (Figure 1).
Figure 1.

Box plots showing the initial and critical (germination imminent) E : S (embryo length to seed length) ratios. The lower vertical line is the minimum value, the bottom line of the box is first quartile, the bold horizontal line is the median, the top line of the box is the third quartile, and the upper vertical line is the maximum value. The black dots are outliers.
Germination
For germination under the different conditions (except for the dark control seeds sown in darkness and not checked for 61 days), mean (± SE) parameter estimates ranged as follows: d (the maximum proportion germinated) from 0.78% ± 0.07 (at 25/15°C in light) to 0.94% ± 0.07 (at 20/10°C in light), t 50 (time to 50% germination) from 19.86 days ± 2.50 (at 20/10°C in light) to 25.53 days ± 2.97 (at 25/15°C in darkness), and b (absolute value proportional to slope) from −7.76 ± 2.17 (at 20/10°C in light) to −3.07 ± 0.97 (at 15/5°C in light; Table 1, Figure 2). There were no significant differences between any germination conditions for d (P > 0.10) or t 50 (P > 0.10). The parameter estimate b for 20/10°C in light was significantly higher (steeper) to that of parameter estimate b of 25/15°C in darkness (P = 0.04; Table 2, Figure 2, Appendix 1).
Table 1.
Parameter estimates for d (maximum germination), absolute value b (proportional to the slope; higher absolute value equals steeper slope and thus a higher rate), and time to 50% germination (t 50) with standard error (SE).
| Germination conditions | Parameter | Estimate | SE |
|---|---|---|---|
| 15/5°C light/dark | d | 0.9263 | 0.0983 |
| 20/10°C light/dark | d | 0.9400 | 0.0683 |
| 25/15°C darka | d | 0.8701 | 0.0655 |
| 25/15°C light/dark | d | 0.7808 | 0.0669 |
| 15/5°C light/dark | b | −3.1827 | 0.9663 |
| 20/10°C light/dark | b | −7.7586 | 2.1724 |
| 25/15°C darka | b | −3.0703 | 0.6004 |
| 25/15°C light/dark | b | −4.3330 | 0.7972 |
| 15/5°C light/dark | t 50 | 23.3847 | 2.0246 |
| 20/10°C light/dark | t 50 | 19.8582 | 2.4959 |
| 25/15°C darka | t 50 | 25.5297 | 2.9711 |
| 25/15°C light/dark | t 50 | 20.0158 | 2.2187 |
Used safe green light.
Figure 2.

Germination time courses for seeds of Brighamia rockii under various incubation conditions. ▼indicates dark‐germination without the use of the safe green light.
Table 2.
Pairwise comparison of the different germination conditions and corresponding P values for parameter estimates b (absolute value proportional to the slope), d (maximum proportion germinated), and t 50 (time to 50% germination).
| Pairwise germination condition comparison | P value | ||
|---|---|---|---|
| d | b | t 50 | |
| 15/5°C light/dark vs. 20/10°C light/dark | 0.9093 | 0.0543 | 0.2725 |
| 15/5°C light/dark vs. 25/15°C darka | 0.6340 | 0.9212 | 0.5508 |
| 15/5°C light/dark vs. 25/15°C light/dark | 0.2212 | 0.3585 | 0.2620 |
| 20/10°C light/dark vs. 25/15°C darka | 0.4603 | 0.0375 | 0.1439 |
| 20/10°C light/dark vs. 25/15°C light/dark | 0.0962 | 0.1388 | 0.9624 |
| 25/15°C darka vs. 25/15°C light/dark | 0.3405 | 0.2058 | 0.1370 |
Used safe green light.
A set of dark control seeds were sown in complete darkness, incubated at 25/15°C, and not checked for 61 days to compare their germination against the dark‐grown seeds checked under the safe green light. Of the 50 dark control seeds sown, 24 (48%) germinated. By contrast, the seeds incubated in the dark at 25/15°C and exposed to green light during germination monitoring had a germination rate of 87% ± 0.07.
DISCUSSION
We showed that the embryos grew inside the seeds of B. rockii prior to their germination; thus, they have MD or MPD. Both MD and MPD have been identified in other members of Hawaiian Campanulaceae; for example, MD and/or MPD was found in Delissea Gaudich. (two species), Clermontia Gaudich. (10 species), and Lobelia L. (seven species), but only MPD was found in Cyanea Gaudich. (four species) and Trematolobelia Zahlbr. ex Rock (three species) (Baskin et al., 2005, 2020; Baskin and Baskin, 2014). We did not observe any significant difference in the final germination or t 50 between any of the temperature and light regimes, and t 50 was reached in 19−26 days, which suggests that seeds of B. rockii have MD. It is important to note, however, that 84 days elapsed between seed collecting and testing, which for some species is ample time for physiological dormancy to be broken via after‐ripening (Baskin and Baskin, 2020). A Hawaiian gardening handbook states that seeds of the genus Brighamia will germinate within 10 days to three months in nursery conditions (Lilleeng‐Rosenberger, 2005); however, for one accession of B. insignis (20180161) from NTBG, seeds sown 13 days after collection and incubated in a 25/15°C 12 h light/12 h dark regime germinated between 33–67 days later, reaching 70% germination. In another B. insignis accession (20180199) from NTBG, only one of the seeds sown eight days after collection at 25/15°C 12 h light/12 h dark regime germinated within 44 days after sowing, and by day 98, germination had ended at just 22%. By contrast, we found that seeds of this same accession stored for one year at the recommended storage conditions for desiccation‐tolerant freeze‐sensitive species (e.g., a target equilibrium relative humidity of 20% at the storage temperature of 5°C; Chau et al., 2019) sown under the same conditions had a 70% germination rate in a 34–89‐day period, except for one seed that germinated on day 117 (Wolkis, unpublished data); thus, our study has not eliminated the possibility that at least some B. rockii seeds have MPD. The time period over which fresh Brighamia seeds are reported to germinate (e.g., 10 days to three months) seems to suggest that a seed lot consists of a mixture of seeds with MD and MPD, and that those with MPD undergo after‐ripening to break the physiological component of MPD. Clearly, more research is needed to determine whether seeds of B. rockii have MD, MPD, or a mixture of both.
For studies of most Hawaiian Campanulaceae species in which multiple temperature regimes were used, high germination percentages occurred at 25/15°C (e.g., for Clermontia fauriei H. Lév., C. hawaiiensis Rock, C. kakeana Meyen, Cyanea angustifolia (Cham.) Hillebr., C. kunthiana Hillebr., Delissea rhytidosperma H. Mann, Lobelia grayana E. Wimm., L. hypoleuca Hillebr., and Trematolobelia macrostachys (Hook. & Arn.) Zahlbr. ex Rock). An exception was Clermontia pyrularia Hillebr., which germinated only at 15/6°C (Baskin et al., 2005, 2020). Here, we showed that a high germination percentage also occurred for B. rockii at 25/15°C, but this was not significantly different from the other two temperatures at which seeds were tested (15/5°C and 20/10°C).
The seeds incubated in continuous darkness at 25/15°C for 61 days had a 48% germination rate, while those incubated in darkness but exposed to green safe light at this temperature regime had an 87% germination rate after 96 days, suggesting that the safe green light did promote germination of some B. rockii seeds. The germination of seeds in continuous darkness (without exposure to the safe green light) suggests that this species is unlikely to form a long‐lasting soil seed bank; however, more studies are needed to determine whether this is the case in their natural habitat. If the seeds germinate while buried, this would lead to the loss of a viable soil seed bank. In a recent case study using the only other species in the genus, B. insignis, the authors recommend implementing a pedigree‐based approach to management of reproduction of plants ex situ to slow the inevitable loss of genetic diversity and, in turn, result in healthier collections (Foster et al., 2022). As B. rockii is held in ex situ collections in at least four locations in Hawaiʻi (Walsh et al., 2022), it is expected that B. rockii should be managed with the same approach.
Recently, Pence et al. (2022a) updated the definition of an exceptional species to: “plant species that cannot be efficiently and effectively conserved long‐term ex situ under the conditions of conventional seed banking, requiring modified approaches,” and outlined a set of conditions as exceptionality factors. Exceptionality factor 1 (EF1) is that seeds are not produced or are extremely limited in quantity, viability, or accessibility. Exceptionality factor 2 (EF2) states that seeds cannot survive drying to ca. 15% RH. Under exceptionality factor 3 (EF3), seeds may be desiccation tolerant, but their viability will decline to 50% (P50) in <20 years. In exceptionality factor 4 (EF4), seeds are deeply dormant with very long germination times (>1 year), and germination has not yet been successful with any conventional dormancy‐breaking method (Pence et al., 2022a). Dianella sandwicensis Hook. & Arn. and Osteomeles anthyllidifolia (Sm.) Lindl. are examples of EF4 species that co‐occurred with B. rockii on Huelo Islet before that species was extirpated there, whose seeds have deep MPD and intermediate or deep PD, respectively (Wolkis et al., 2018; Baskin et al., 2021). Seeds of D. sandwicensis reached 50% germination at 20/10°C and 20/15°C in 20 weeks (Wolkis et al., 2018), and those of O. anthyllidifolia reached 50% germination at 25/15°C and 20/10°C in 17 weeks (Baskin et al., 2021). By contrast, we showed that the B. rockii seeds reached 50% germination in 20–26 days. These results provide the empirical data needed to verify the findings of a recent exceptional species gap analysis, which indicated that Brighamia seeds do not fit under EF4 (but are correctly classified as EF3 as described above; Pence et al., 2022b; list available at http://cincinnatizoo.org/global-list-of-threatened-exceptional-plants [accessed 4 August 2022]).
For many exceptional species, cryobiotechnologies (and, to some extent, in vitro propagation) have been the main focus of preservation research (Pritchard, 2018; Pence et al., 2020; Philpott et al., 2022), but the storage of dry seeds at −18°C would be less expensive than cryobiotechnology. However, seeds of various species, including those of some EF3 species with intermediate storage behavior such as Brighamia, do not survive the long‐term combined stresses of desiccation and freezing at −18°C. Triacylglycerol (TAG) has been identified in seeds of the majority of species with intermediate storage behavior, and its crystallization at conventional storage temperatures (−18°C) in diverse species may be an important cause of damage that results in the loss of seed viability (Ballesteros et al., 2020). One possible technological innovation, especially for EF3 species, might be to store the desiccated seeds at −80°C, but this method has not been tested. Lipid thermal fingerprinting could be used to identify biophysical markers in relation to storage stability at different temperatures (e.g., Mira et al., 2019) including −80°C; this would give insight into whether EF3 species could be stored safely at −80°C, making this temperature a viable alternative to cryobiotechnology. Until more is known about lipid thermal properties or viability after storage at −80°C, it is recommended that B. rockii seeds are desiccated to 20% RH at a storage temperature of +5°C (Chau et al., 2019).
Brighamia rockii seeds stored for 12 weeks have high germination over a range of temperature regimes in light and at 25/15°C in darkness (the only dark temperature tested). Thus, this exceptional species can be propagated from seeds for conservation purposes. The ability of many seeds of this species to germinate in darkness suggests that it is unlikely to form a long‐lived soil seed bank; therefore, the re‐establishment of extirpated populations will require reintroduction. Brighamia rockii seeds have either MD or MPD or a mixture thereof, and more research is needed to determine the class(es) of dormancy in this species.
AUTHOR CONTRIBUTIONS
D.W., C.C.B., J.M.B., and N.R. conceptualized the study. D.W. designed and conducted the germination studies, statistical analyses, and drafted the manuscript. All authors read and approved the final version of the manuscript.
Supporting information
Appendix S1. Germination data for Brighamia rockii.
ACKNOWLEDGMENTS
The authors thank the Hawaiʻi State Department of Land and Natural Resources for Natural Area Reserve, Rare Plant, and Native Invertebrate Research (permit numbers I1287, I2499, I2463, and I2808); Anna Palomino and Ane Bakutis (Hawaiʻi Plant Extinction Prevention Program; University of Hawaiʻi Center for Conservation Research and Training; Hawaiʻi State Department of Land and Natural Resources Department of Forestry and Wildlife) for collecting and shipping the seeds, respectively; Ane Bakutis and Matthew Keir (Hawaiʻi State Department of Land and Natural Resources Department of Forestry and Wildlife) for their permission to use NTBG accession 20200568 in this research; National Tropical Botanical Garden interns and volunteers Jeffrey Frelinger, Kelli Jones, and Leslie Ridpath for their assistance in monitoring germination; Seana Walsh at National Tropical Botanical Garden for helpful discussions about Brighamia; and the handling editor and two anonymous reviewers whose time and effort improved the manuscript.
Wolkis, D. , Baskin C. C., Baskin J. M., and Rønsted N.. 2022. Seed dormancy and germination of the endangered exceptional Hawaiian lobelioid Brighamia rockii . Applications in Plant Sciences 10(5): e11492. 10.1002/aps3.11492
This article is part of the special issue “Meeting the Challenge of Exceptional Plant Conservation: Technologies and Approaches.”
DATA AVAILABILITY STATEMENT
The data that support the findings of this study are included as Appendix S1.
REFERENCES
- Ballesteros, D. , Pritchard H. W., and Walters C. T.. 2020. Dry architecture: Towards the understanding of the variation of longevity in desiccation‐tolerant germplasm. Seed Science Research 30: 142–155. [Google Scholar]
- Baskin, C. C. , and Baskin J. M.. 2014. Seeds: Ecology, biogeography and evolution of dormancy and germination, 2nd ed. Elsevier/Academic Press, San Diego, California, USA. [Google Scholar]
- Baskin, C. C. , and Baskin J. M.. 2020. Breaking seed dormancy during dry storage: A useful tool or major problem for successful restoration via direct seeding? Plants 9: 636. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Baskin, C. C. , Baskin J. M., and Yoshinaga A. Y.. 2005. Morphophysiological dormancy in seeds of six endemic lobelioid shrubs (Campanulaceae) from the montane zone in Hawaii. Canadian Journal of Botany 83: 1630–1637. [Google Scholar]
- Baskin, C. C. , Thompson K., and Baskin J. M.. 2006. Mistakes in germination ecology and how to avoid them. Seed Science Research 16: 165–168. [Google Scholar]
- Baskin, C. C. , Baskin J. M., Yoshinaga A., and Wolkis D.. 2020. Seed dormancy in Campanulaceae: Morphological and morphophysiological dormancy in six species of Hawaiian lobelioids. Botany 98: 327–332. [Google Scholar]
- Baskin, C. C. , Baskin J. M., Yoshinaga A. Y., and Wolkis D.. 2021. Physiological dormancy in seeds of tropical montane woody species in Hawaiʻi. Plant Species Biology 36: 60–71. [Google Scholar]
- Chau, M. M. , Chambers T., Weisenberger L., Keir M., Kroessig T. I., Wolkis D., Kam R., and Yoshinaga A. Y.. 2019. Seed freeze sensitivity and ex situ longevity of 295 species in the native Hawaiian flora. American Journal of Botany 106: 1248–1270. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Cochrane, A. , Crawford A. D., and Monks L. T.. 2007. The significance of ex situ seed conservation to reintroduction of threatened plants. Australian Journal of Botany 55: 356–361. [Google Scholar]
- Convention on Biological Diversity . 2011. Secretariat of the Global Strategy for Plant Conservation. Website: https://www.cbd.int/gspc/ [accessed 30 June 2022].
- Foster, J. A. , Walsh S. K., Havens K., Kramer A. T., and Fant J. B.. 2022. Supporting long‐term sustainability of ex situ collections using a pedigree‐based population management approach. Applications in Plant Sciences 10(5): e11491. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Giambelluca, T. W. , Shuai X., Barnes M. L., Alliss R. J., Longman R. J., Miura T., Chen Q., et al. 2014. Evapotranspiration of Hawaiʻi. Final report submitted to the U.S. Army Corps of Engineers—Honolulu District, and the Commission on Water Resource Management, State of Hawaiʻi. Available at: http://evapotranspiration.geography.hawaii.edu/ [accessed 30 June 2022].
- Givnish, T. J. , Millam K. C., Mast A. R., Paterson T. B., Theim T. J., Hipp A. L., Henss J. M., et al. 2009. Origin, adaptive radiation and diversification of the Hawaiian lobeliads (Asterales: Campanulaceae). Proceedings of the Royal Society B: Biological Sciences 276: 407–416. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Guerrant, E. O. , Havens K., and Maunder M. [eds.]. 2004. Ex situ plant conservation supporting species survival in the wild. Island Press, Washington, D.C., USA. [Google Scholar]
- Humphreys, A. M., R. Govaerts, S. Z. Ficinski, E. Nic Lughadha, and Vorontsova M. S.. 2019. Global dataset shows geography and life form predict modern plant extinction and rediscovery. Nature Ecology & Evolution 3: 1043–1047. [DOI] [PubMed] [Google Scholar]
- Intergovernmental Science‐Policy Platform on Biodiversity and Ecosystem Services (IPBES) . 2019. Global assessment report on biodiversity and ecosystem services. In: Brondizio E. S., Settele J., Díaz S., and Ngo H. T. [eds.]. IPBES, Bonn, Germany. [Google Scholar]
- Jensen, S. M. , Andreasen C., Streibig J. C., Keshtkar E., and Ritz C.. 2017. A note on the analysis of germination data from complex experimental designs. Seed Science Research 27: 321–327. [Google Scholar]
- Jensen, S. M. , Wolkis D., Keshtkar E., Streibig J. C., and Ritz C.. 2020. Improved two‐step analysis of germination data from complex experimental designs. Seed Science Research 30: 194–198. [Google Scholar]
- Lilleeng‐Rosenberger, K. E. 2005. Growing Hawaiʻi's native plants. Mutual Publishing, Honolulu, Hawaiʻi, USA. [Google Scholar]
- Liu, U. , Breman E., Cossu T. A., and Kenney S.. 2018. The conservation value of germplasm stored at the Millennium Seed Bank, Royal Botanic Gardens, Kew, UK. Biodiversity and Conservation 27: 1347–1386. [Google Scholar]
- Liu, U. , Cossu T. A., Davies R. M., Forest F., Dickie J. B., and Breman E.. 2020. Conserving orthodox seeds of globally threatened plants ex situ in the Millennium Seed Bank, Royal Botanic Gardens, Kew, UK: The status of seed collections. Biodiversity and Conservation 29: 2901–2949. [Google Scholar]
- Mira, S. , Nadarajan J., Liu U., González‐Benito M. E., and Pritchard H. W.. 2019. Lipid thermal fingerprints of long‐term stored seeds of Brassicaceae. Plants 8: e414. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Pence, V. C. , Ballesteros D., Walters C. T., Reed B. M., Philpott M., Dixon K. W., Pritchard H. W., et al. 2020. Cryobiotechnologies: Tools for expanding long‐term ex situ conservation to all plant species. Biological Conservation 250: 108736. [Google Scholar]
- Pence, V. C. , Meyer A., Linsky J., Gratzfeld J., Pritchard H. W., Westwood M., and Bruns E. B.. 2022a. Defining exceptional species—A conceptual framework to expand and advance ex situ conservation of plant diversity beyond conventional seed banking. Biological Conservation 266: 109440. [Google Scholar]
- Pence, V. C. , Bruns E. B., Meyer A., Pritchard H. W., Westwood M., Linsky J., Gratzfeld J., et al. 2022b. Gap analysis of exceptional species—Using a global list of exceptional plants to expand strategic ex situ conservation action beyond conventional seed banking. Biological Conservation 266: 109439. [Google Scholar]
- Phartyal, S. S. , Thapliyal R. C., Koedam N., and Godefroid S.. 2002. Ex situ conservation of rare and valuable forest tree species through seed‐gene bank. Current Science 83: 1351–1357. [Google Scholar]
- Philpott, M. , Pence V. C., Bassüner B., Clayton A. S., Coffey E. E. D., Downing J. L., Edwards C. E., et al. 2022. Harnessing the power of botanical gardens: Evaluating the costs and resources needed for exceptional plant conservation. Applications in Plant Sciences 10(5): e11495. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Pritchard, H. W. 2018. The rise of plant cryobiotechnology and demise of plant cryopreservation? Cryobiology 85: 160–161. [Google Scholar]
- R Core Team . 2021. R: A language and environment for statistical computing. R Foundation for Statistical Computing, Vienna, Austria. Website: http://www.R-project.org/ [accessed 30 June 2022]. [Google Scholar]
- Ritz, C. , Pipper C. B., and Streibig J. C.. 2013. Analysis of germination data from agricultural experiments. European Journal of Agronomy 45: 1–6. [Google Scholar]
- Ritz, C. , Jensen S. M., Gerhard D., and Streibig J. C.. 2019. Analysis of dose‐response germination data using R. CRC Press, Boca Raton, Florida, USA. [Google Scholar]
- Rønsted, N. , Walsh S. K., Clark M., Edmonds M., Flynn T., Heintzman S., Loomis A., et al. 2022. Extinction risk of the endemic vascular flora of Kauai, Hawaii, based on IUCN assessments. Conservation Biology 36: e13896. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Royal Botanic Gardens Kew . 2020. Seed Information Database (SID). Version 7.1. Website: http://data.kew.org/sid [accessed 30 June 2022].
- RStudio Team . 2019. RStudio: Integrated Development for R. RStudio, PBC, Boston, Massachusetts, USA. Website: http://www.rstudio.com/ [accessed 30 June 2022].
- United States Fish and Wildlife Service . 2016. ECOS Environmental Conservation Online System, Species occurrence by state. Website: https://ecos.fws.gov/ecp/ [accessed 15 October 2020].
- Wagner, W. L. , Herbst D., and Sohmer S.. 1999. Manual of the flowering plants of Hawaiʻi, revised edition. University of Hawaiʻi Press and Bishop Museum Press, Honolulu, Hawaiʻi, USA. [Google Scholar]
- Wagner, W. L. , Herbst D. R., and Lorence D. H.. 2005. Flora of the Hawaiian Islands website. Website: http://botany.si.edu/pacificislandbiodiversity/hawaiianflora/index.htm [accessed 30 June 2022].
- Walsh, S. K. , Opgenorth M., Keir M. J., Nyberg B., and Wood K. R.. 2022. Brighamia rockii. The IUCN Red List of Threatened Species 2022: e.T44081A83789301. Website: 10.2305/IUCN.UK.2022-1.RLTS.T44081A83789301.en [accessed 5 August 2022]. [DOI]
- Walsh, S. K. , Pender R. J., Junker R. R., Daehler C. C., Morden C. W., and Lorence D. H.. 2019. Pollination biology reveals challenges to restoring populations of Brighamia insignis (Campanulaceae), a critically endangered plant species from Hawaiʻi. Flora 259: 151448. [Google Scholar]
- Wickham, H. 2016. ggplot2: Elegant Graphics for Data Analysis. Springer‐Verlag, New York, New York, USA. [Google Scholar]
- Wolkis, D. , Baskin C. C., and Baskin J. M.. 2018. Dormancy‐breaking and germination requirements of seeds of the Hawaiian endemic Dianella sandwicensis (Xanthorrhoeaceae). Australian Journal of Botany 66: 213–217. [Google Scholar]
- Wood, K. R. , Oppenheimer H., and Keir M.. 2019. A checklist of endemic Hawaiian vascular plant taxa that are considered possibly extinct in the wild. National Tropical Botanical Garden, Technical Report #314. Available at: https://www.researchgate.net/publication/332916448_A_checklist_of_endemic_Hawaiian_vascular_plant_taxa_that_are_considered_possibly_extinct_in_the_wild [accesssed 5 August 2022].
Associated Data
This section collects any data citations, data availability statements, or supplementary materials included in this article.
Supplementary Materials
Appendix S1. Germination data for Brighamia rockii.
Data Availability Statement
The data that support the findings of this study are included as Appendix S1.
