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Seed dormancy and germination in Myrtaceae: a palaeohistory, tribe, life cycle and geographical distribution perspective

Published online by Cambridge University Press:  16 April 2025

Carol C. Baskin*
Affiliation:
Department of Biology, University of Kentucky, Lexington, KY 40506-0225, USA Department of Plant and Soil Sciences, University of Kentucky, Lexington, KY 40506-0312, USA
Jerry M. Baskin
Affiliation:
Department of Biology, University of Kentucky, Lexington, KY 40506-0225, USA
*
Corresponding author: Carol C. Baskin; Email: [email protected]
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Abstract

The Myrtaceae is the ninth largest angiosperm family with c. 6000 species, and it diverged from its closest relative the Vochysiaceae c. 100 Ma in southern Gondwana before the final separation of South America and Australia from Antarctica. The family has trees and shrubs and a few viny epiphytes but no herbs and mainly occurs in the tropics and in temperate regions with a Mediterranean climate. Numerous fleshy-fruited species and dry-fruited species have evolved in moist and seasonally dry (fire-prone) regions, respectively. Five kinds of fully developed embryos are found in Myrtaceae seeds, and at maturity seeds are either nondormant (ND) or have physiological dormancy, regardless of embryo morphology, kind of fruit produced, life form, habitat/vegetation region or tribe. Dormant seeds of fleshy-fruited species in wet habitats become ND and germinate at high temperatures. Dormant seeds of dry-fruited species in seasonally dry habitats become ND during the hot, dry season and germinate with the onset of the wet season; seeds germinate only at high temperatures or over a range of low to high temperatures, depending on the species. Seeds of fleshy-fruited species are animal-dispersed, and some Myrteae and Syzygieae are desiccation-sensitive and/or exhibit totipotency. Relatively few species form a persistent soil seed bank, but many dry-fruited species in fire-prone habitats form an aerial seed bank (serotiny). Heat and smoke from fires have a negative, neutral or positive effect on germination, depending on the species. Challenges for maintaining the high species richness of Myrtaceae include habitat destruction/fragmentation, pathogenic fungi and climate change, especially patterns of precipitation.

Type
Review Paper
Creative Commons
Creative Common License - CCCreative Common License - BY
This is an Open Access article, distributed under the terms of the Creative Commons Attribution licence (http://creativecommons.org/licenses/by/4.0/), which permits unrestricted re-use, distribution and reproduction, provided the original article is properly cited.
Copyright
Copyright © The Author(s), 2025. Published by Cambridge University Press

Introduction

The purpose of this review is to further explore the relationship between kinds of seed dormancy/germination, embryo morphology, life form, geographical distribution, habitats (vegetation regions on Earth) and phylogeny in angiosperm plant families. In particular, what do highly speciose, widely distributed families have in common, and how do they differ from families with a low number of species and a narrow geographical distribution? If a speciose family is widely distributed geographically, how diverse is it with regard to kinds of seed dormancy, life form and vegetation in regions in which it grows? These questions can be answered only after we have documented the kinds of seed dormancy in plant families that differ in number of species, habitats and geographical range. As a contribution to the broad objective of understanding the diversity of seed dormancy/germination in angiosperm plant families, we have reviewed available information on the Myrtaceae.

The Myrtaceae is highly speciose and is widely distributed in the Southern Hemisphere, and we have addressed nine specific questions. (1) What kinds of embryos do seeds of Myrtaceae have, and how are they distributed in the tribes of this family? (2) What kinds of seed dormancy, including nondormancy, are found in the Myrtaceae, and what is their occurrence in the tribes and life forms of this family? (3) What is the seed dormancy profile for Myrtaceae in the various vegetation regions where species of the family grow? (4) What environmental conditions are required for dormancy-break and germination of seeds? (5) How many tribes and species of Myrtaceae have desiccation-sensitive seeds? (6) In the totipotent (i.e. plantlet production from seed fragments) species of Myrtaceae, how many plantlets can be produced from a single seed? (7) How is the germination of Myrtaceae seeds affected by the heat and smoke of fires? (8) What is the relative importance of soil and aerial seed banks for Myrtaceae? (9) What are the major challenges involved in maintaining the high species richness of Myrtaceae in the future? However, before considering these questions, information will be provided on the general characteristics, palaeohistory and reproductive biology of Myrtaceae.

General characteristics of Myrtaceae

de Candolle (Reference de Candolle1828) divided the Myrtaceae into three tribes: Myrteae (with fleshy berries), Leptospermeae (dry dehiscent loculicidal capsules) and Chamelaucieae (dry indehiscent capsules). The genera Heteropyxis and Psiloxylon have been placed in the Heteropyxidaceae and Psiloxylaceae, respectively (e.g. Johnson and Briggs, Reference Johnson and Briggs1984). However, Scott (Reference Scott1980) concluded that Psiloxylon belonged to the Myrtaceae, and Tobe and Raven (Reference Tobe and Raven1987, Reference Tobe and Raven1990) found embryological evidence that Heteropyxis and Psiloxylon shared a single ancestor and suggested that the two genera should be included in the Myrtaceae, or close to it. Based on a matK phylogeny that included 66 genera from all alliances and suballiances of core Myrtaceae, Heteropyxis natalensis and Psiloxylon mauritianium, Wilson et al. (Reference Wilson, O'Brien, Heslewood and Quinn2005) concluded that there are two subfamilies of Myrtaceae: Psiloxyloideae with tribes Heteropyxideae and Psiloxyleae and Myrtoideae with 15 tribes. Three additional tribes have been distinguished for the Myrtoideae, making a total of 18 in this subfamily (Wilson et al., Reference Wilson, Heslewood and Tarran2022): Backhousieae, Chamelaucieae, Cloezieae, Eucalypteae, Kanieae, Leptospermeae, Lindsayomyrteae, Lophostemoneae, Melaleuceae, Metrosidereae, Myrteae, Osbornieae, Syncarpieae, Syzygieae, Tristanieae, Tristaniopsideae, Xanthomyrteae and Xanthostemoneae.

The Myrtaceae has 126 accepted genera and c. 6000 species (POWO; Landrum, Reference Landrum2021) and is the ninth-largest family of angiosperms (Govaerts et al., Reference Govaerts, Sobral, Ashton and Barrie2008). Fourteen tribes with 70 genera and c. 1700 species occur in Australia (Thornhill et al., Reference Thornhill, Ho, Külheim and Crips2015; Hardstaff et al., Reference Hardstaff, Sommerville, Funnekotter, Bunn and Offord2022). In contrast, species richness in the Neotropics is due mostly to the tribe Myrteae with 51 genera and c. 2500 species (Wilson et al., Reference Wilson, O'Brien, Heslewood and Quinn2005; Lucas et al., Reference Lucas, Harris, Mazine, Belsham, Nic Lughadha, Telford, Gasson and Chanse2007; Vasconcelos et al., Reference Vasconcelos, Proença, Ahmad, Aguilar, Aguilar, Amorium, Campbell, Costa, Mazine, Peguero, Prenner, Santos, Soewarto, Wingler and Lucas2017). At least 15 genera (Archirhodomyrtus, Austromyrtus, Decaspermum, Gossia, Lenwebbia, Lithomyrtus, Lophomyrtus, Myrtella, Myrtuastrum, Neomyrtus, Octamyrtus, Pilidiostigma, Rhodamnia, Rhodomyrtus and Uromyrtus) and c. 450 species of Myrteae occur outside the Neotropics, including Southeast Asia, northeastern Australia and Pacific Islands (Wilson, Reference Wilson and Kubitzki2010). Outside the Neotropics, Eugenia is found in Africa, Madagascar and Mauritius (Snow, Reference Snow2000; van der Merwe et al., Reference van der Merwe, van Wyk and Botha2005).

Various species of this family are used as ornamentals, medicines or food by humans (Hardstaff et al., Reference Hardstaff, Sommerville, Funnekotter, Bunn and Offord2022). Species in about 20 genera of Myrtaceae have been introduced into parts of the world beyond their natural range and are considered to be invasive (Mbobo et al., Reference Mbobo, Richardson, Lucas and Wilson2022). Both dry- (e.g. Eucalyptus) and fleshy- (e.g. Psidium) fruited species can be invasive, and fleshy-fruited species are more likely to be invasive on islands than dry-fruited species (Mbobo et al., Reference Mbobo, Richardson, Lucas and Wilson2022).

With the exception of Myrtus in northern Africa and the Mediterranean region of southern Europe (Wilson, Reference Wilson and Kubitzki2010), the Myrtaceae is mostly a tropical family with high species richness in South America and Australia; it also occurs in Africa, Southeast Asia, India and on various Pacific Islands (Wilson, Reference Wilson and Kubitzki2010; Thornhill et al., Reference Thornhill, Ho, Külheim and Crips2015). The family consists of trees, shrubs and a few subshrubs and strangling (viny) epiphytes (e.g. some species of Metrosideros). The monotypic shrub/small tree Osbornia octodonta is a mangrove, but it does not have pneumatophores. The leaves and stems of Myrtaceae have secretory cavities and lysigenous glands that produce ethereal oils, making plants (e.g. Eucalyptus) aromatic (Wilson, Reference Wilson and Kubitzki2010).

Flowers of Myrtaceae are actinomorphic and (0-) 4 or 5 (-7)-merous with numerous (10–270) stamens that may be in fascicles opposite the petals. Flowers of Eucalyptus and Corymbia have an operculum (bud cover) that opens at anthesis and then falls from the flower (Mabberley, Reference Mabberley2017). In some species, the stamen display attracts pollinators that collect pollen, but in other species, the thick and sweet petals are the attraction for pollinators. Flowers have a hypanthium, and the ovary may be superior, inferior or half-interior. There is one pistil, and the ovary is 1-6[-18] locular and carpellate. Placentation is axile, basal or parietal with 2–300(-500) ovules in the ovary (Wilson, Reference Wilson and Kubitzki2010; Vasconcelos et al., Reference Vasconcelos, Prenner and Lucas2019; Landrum, Reference Landrum2021).

Wilson (Reference Wilson and Kubitzki2010) described six general kinds of fruits/dispersal units for the Myrtaceae: (1) three-loculed soft fruit or berry developed from a superior ovary, Psiloxylon; (2) fruit with an inferior ovary and fleshy hypanthium, usually called a ‘berry’, Syzygieae; (3) drupe-like fruits with a thin fleshy covering over a mass of seeds with bony seed coats, Myrtella and Lithomyrtus; (4) indehiscent, leathery fruit, Osbornia; (5) dry, indehiscent fruits (‘nut-like’), Chamelaucium, Corynanthera and Thryptomene and (6) dry, dehiscent capsule, Leptospermeae and Melaleuceae. Seeds of Myrtaceae have little or no endosperm. The embryo in mature seeds is starchy or oily, fully developed (does not grow inside the seed prior to initiation of germination) and may be straight, coiled or folded (Zomlefer, Reference Zomlefer1994; Snow, Reference Snow2000; Simpson, Reference Simpson2006; Wilson, Reference Wilson and Kubitzki2010; Retamales et al., Reference Retamales, Cabello, Serra and Scharaschkin2014; Ribeiro et al., Reference Ribeiro, Nascimento, Cruz and Gurgel2021; Neto et al., Reference Neto, Santos, Lucas, Veto, Barrientos-Diaz, Staggemeier, Vasconcelos and Turchetto-Zolet2022). The seed coat may be membranous, bony or somewhat leathery, depending on the tribe/genus (Corner, Reference Corner1976; Landrum and Sharp, Reference Landrum and Sharp1989; Retamales et al., Reference Retamales, Cabello, Serra and Scharaschkin2014; Ribeiro et al., Reference Ribeiro, Nascimento, Cruz and Gurgel2021; Sbais et al., Reference Sbais, Machado, Valdemarin, Thadeo, Mazine and Mourão2022), but it does not have a palisade layer of Malpighian cells, i.e. specialized macrosclereids with a light line that are found in water-impermeable seeds (Corner, Reference Corner1976; Werker, Reference Werker1997). Seeds are 0.5–20 mm in length, depending on the species (Kirkbride et al., Reference Kirkbride, Gunn and Dallwitz2006).

Palaeohistory of Myrtaceae

Berger et al. (Reference Berger, Kriebel, Spalink and Sytsma2016) reported that the Myrtales diverged from the Geraniales c. 124 Ma with a crown age of c. 116 Ma and that the Myrtales originated in West Gondwana (i.e. South America and Africa). However, Zhang et al. (Reference Zhang, Landis, Wang, Zhu and Wang2021) concluded that the Myrtales differentiated from the Geraniales c. 111.5 Ma with a crown age of c. 104.9 Ma. Laurasia had separated from Gondwana at 116–104.9 Ma, and the southern and central parts of South America and Africa separated between 135 to 105 and 119 to 105 Ma, respectively (McLoughlin, Reference McLoughlin2001). Based on data from studies on molecular phylogeny, the divergence of the Myrtaceae has been placed at 85 (Thornhill et al., Reference Thornhill, Ho, Külheim and Crips2015; Berger et al., Reference Berger, Kriebel, Spalink and Sytsma2016) to 80 Ma (Sytsma et al., Reference Sytsma, Litt, Zjhra, Pires, Nepokroeff, Conti, Walker and Wilson2004), which was before the final separation of South America from Antarctica and the separation of Australia from Antarctica c. 30 Ma with opening of the Drake Passage and Tasman Straight, respectively (Scotese and Golonka, Reference Scotese and Golonka1992; Lawver and Gahagan, Reference Lawver and Gahagan2003; Scotese, Reference Scotese2021). However, Gonçalves et al. (Reference Gonçalves, Shimizu, Ortiz, Jansen and Simpson2020) used data for 78 plastid protein-coding genes from 125 species representing 8 myrtalean families, including 8 genera and 51 species of Vochysiaceae, and fossils from 4 myrtalean families and estimated the crown age of Myrtales as 125.5 Ma. These authors placed the divergence of Myrtaceae from its closest relative the Vochysiaceae at c. 100 Ma with a stem age of 115 Ma. Based on these dates, the Myrtaceae diverged before the beginning of the separation of West Gondwana and South America.

Hill and Scriven (Reference Hill and Scriven1995) and McLoughlin (Reference McLoughlin2001) concluded that the disturbance caused by continental rifting may have provided new environmental conditions that promoted the diversification and dispersal of angiosperms, including the Myrtaceae. Jordan et al. (Reference Jordan, Barraclough and Rosindell2016) thought that continental movements probably do not explain the increase in a number of terrestrial species but that changes in climates due to the movements of continents may have promoted increased speciation.

Thornhill et al. (Reference Thornhill, Ho, Külheim and Crips2015) reported that Myrtaceae had a Gondwanan origin and that at least 6 of the 22 sister groups of this family included in their study may be a product of vicariance. Three of the 22 sister groups had evidence of overland dispersal events, while the other 13 had undergone transoceanic long-distance dispersal. Some researchers, e.g. Sytsma et al. (Reference Sytsma, Litt, Zjhra, Pires, Nepokroeff, Conti, Walker and Wilson2004), have suggested that the origin of extant Myrtaceae was in Australasia since tribes such as Chamelaucieae, Eucalypteae, Leptospermeae, Lindsayomyrteae, Lophostemoneae, Melaleuceae and Xanthostemoneae are not found in South America or Africa. Thornhill et al. (Reference Thornhill, Ho, Külheim and Crips2015) suggested that radiation of subfamily Myrtoideae occurred in the part of Gondwana that eventually became Australia. Berger et al. (Reference Berger, Kriebel, Spalink and Sytsma2016) found a significant increase in diversification rates in Myrtaceae at c. 75 Ma, and speciation was 0.32 species Ma−1 and extinction 0.15 species Ma−1. These authors determined that extensive radiation of Myrtaceae occurred in Australia from the Eocene into the Miocene, as the cooling and drying of the climate increased.

The crown age of subfamily Myrtoideae is c. 75 (Biffin et al., Reference Biffin, Lucas, Craven, Costa, Harrington and Crisp2010) to 71.5 Ma (Thornhill et al., Reference Thornhill, Ho, Külheim and Crips2015), and it is c. 39.7 Ma for subfamily Psiloxyloideae (Thornhill et al., Reference Thornhill, Ho, Külheim and Crips2015). The divergence of Heteropyxis and Psiloxylon was c. 18 Ma (Berger et al., Reference Berger, Kriebel, Spalink and Sytsma2016). The crown age of the tribe Myrteae is 50.7 Ma (Thornhill et al., Reference Thornhill, Ho, Külheim and Crips2015), and its likely ancestral area is eastern Gondwana (Australia, New Caledonia, New Guinea and New Zealand) (Vasconcelos et al., Reference Vasconcelos, Proença, Ahmad, Aguilar, Aguilar, Amorium, Campbell, Costa, Mazine, Peguero, Prenner, Santos, Soewarto, Wingler and Lucas2017; Estrella et al., Reference Estrella, Buerki, Vasconcelos, Lucas and Forest2019). The divergence of Australasian and South American Myrteae was 43.9 Ma, after which much radiation occurred in both regions (Thornhill et al., Reference Thornhill, Ho, Külheim and Crips2015). Dispersal events between Australia and South America were possible in the Tertiary via Antarctica (Sytsma et al., Reference Sytsma, Litt, Zjhra, Pires, Nepokroeff, Conti, Walker and Wilson2004).

Fossilized parts of Myrtaceae plants of various ages have been found: flowers, Early Eocene, Argentina (Zamaloa et al., Reference Zamaloa, Gandolfo and Nixon2020); flowers and fruits, Eocene, Australia (Basinger et al., Reference Basinger, Christophel, Greenwood and Wilson2007); fruits and seeds, Eocene, British Columbia (Canada) and Palaeocene, North Dakota (USA) (Pigg et al., Reference Pigg, Stockey and Maxwell1993; Manchester, Reference Manchester1999); leaves, Early Miocene, Australia (Tarran et al., Reference Tarran, Wilson, Paull, Biffin and Hill2018); leaves, Middle Eocene, Argentina (Panti, Reference Panti2016); pollen, Cretaceous–Eocene, Sarawak (Malaysia) (Muller, Reference Muller1968); pollen, Palaeogene–Neogene, Australia (Thornhill and Macphail, Reference Thornhill and Macphail2012); wood, Late Cretaceous–Early Tertiary, Antarctica (Poole et al., Reference Poole, Mennega and Cantrill2003) and wood, Late Cretaceous, India (Shukla et al., Reference Shukla, Mehrotra and Tyagi2012). Fossils can be helpful in dating a phylogeny, but in the case of Myrteae differences in crown mode have resulted, depending on the kind of fossils considered. For example, Vasconcelos et al. (Reference Vasconcelos, Proença, Ahmad, Aguilar, Aguilar, Amorium, Campbell, Costa, Mazine, Peguero, Prenner, Santos, Soewarto, Wingler and Lucas2017) using macrofossils and fossil pollen of Myrteae obtained a crown node for Myrteae of 65.55 Ma (Cretaceous–Palaeocene boundary) and 40.76 Ma (mid-late Eocene), respectively.

Radiation of Myrtaceae resulted in tribes with dry (capsular) fruits and those with fleshy fruits (Thornhill et al., Reference Thornhill, Ho, Külheim and Crips2015). Sytsma et al. (Reference Sytsma, Litt, Zjhra, Pires, Nepokroeff, Conti, Walker and Wilson2004) found that fleshy, indehiscent fruits have originated at least three times in the Myrtaceae: Myrtoid group (Myrteae), Acmena group (Syzygieae) and Osbornia (Osbornieae). Compared with other lineages of Myrtaceae, tribes Syzygieae and Myrteae have had high rates of diversification, and the increased rate is associated with a shift from dry to fleshy fruits, which occurred independently in both tribes (Biffin et al., Reference Biffin, Lucas, Craven, Costa, Harrington and Crisp2010). Nine of the 13 long-distance dispersal events proposed by Thornhill et al. (Reference Thornhill, Ho, Külheim and Crips2015) involved taxa with fleshy fruits that could be dispersed by birds or bats. The presence of Myrtus in the Mediterranean Region perhaps is due to a long-distance dispersal event from East Gondwana to the Mediterranean via northern Africa during the Eocene (Thornhill et al., Reference Thornhill, Ho, Külheim and Crips2015).

Two large genera of Myrtaceae with dry (capsular) fruits are Eucalyptus (tribe Eucalypteae) and Metrosideros (tribe Metrosidereae). The Australasian eucalypt group includes Allosyncarpia, Angophora, Arillastrum, Corymbia, Eucalyptus, Eucalyptopsis and Stockwellia (Ladiges et al., Reference Ladiges, Udovicic and Nelson2003), with Eucalyptus being the largest with 712 species (POWO, 2024). Some species diversification of the Eucalyptus group is related to the cooling and drying of Australia and increased fire frequency (Ladiges et al., Reference Ladiges, Udovicic and Nelson2003). Crisp et al. (Reference Crisp, Burrows, Cook, Thornhill and Bowman2011) reported that the sclerophyllous woodlands and savannas in Australia are dominated by species of Eucalyptus, many of which can resprout after fire. Using trait mapping on a dated phylogeny of Myrtaceae, these authors found that epicormic resprouting (from buds on the stem) in Myrtaceae was correlated with the development of fire-prone Eucalyptus-dominated habitats beginning 60–62 Ma.

Metrosideros with c. 60 species has high richness in Australia, New Caledonia and New Guinea, and it occurs on various Pacific islands such as Bonin, Fiji, Hawaii, Marquesas, New Zealand and Samoa (Wilson, Reference Wilson, Keast and Miller1996; Mabberley, Reference Mabberley2017; Wright et al., Reference Wright, Liddell, Lacap-Bugler and Gillman2021). Metrosideros angustifolia is the only species of Myrtaceae with capsular fruits in Africa (Sytsma et al., Reference Sytsma, Litt, Zjhra, Pires, Nepokroeff, Conti, Walker and Wilson2004; Mabberley, Reference Mabberley2017), and M. stipularis is the only one in the New World (Sytsma et al., Reference Sytsma, Litt, Zjhra, Pires, Nepokroeff, Conti, Walker and Wilson2004). Seeds of Metrosideros are wind dispersed and can be lifted by wind speeds of 5–18 km h−1 (Wright et al., Reference Wright, Yong, Dawson, Whittaker and Gardner2000). Thus, long-distance dispersal by wind may help account for the occurrence of this genus on widely separated Pacific islands.

Except for M. stipularis with dry fruits in Chile and Argentina, all Myrtaceae in the Neotropics belong to the tribe Myrteae and have fleshy fruits (Lucas et al., Reference Lucas, Belsham, Nic Lughadha, Orlovich, Sakuragui, Chase and Wilson2005, Reference Lucas, Matsumoto, Harris, Nic Lughadha, Benardini and Chase2011; Wilson et al., Reference Wilson, O'Brien, Heslewood and Quinn2005; Neto et al., Reference Neto, Santos, Lucas, Veto, Barrientos-Diaz, Staggemeier, Vasconcelos and Turchetto-Zolet2022). Species diversification in Myrteae accelerated in the Neotropics compared with that of Myrteae in the Old World (Vasconcelos et al., Reference Vasconcelos, Proença, Ahmad, Aguilar, Aguilar, Amorium, Campbell, Costa, Mazine, Peguero, Prenner, Santos, Soewarto, Wingler and Lucas2017). The development of new embryo traits [e.g. large storage cotyledons or large leaf-like folded cotyledons) (Landrum, Reference Landrum1986; Landrum and Stevenson, Reference Landrum and Stevenson1986), polyploidy (Costa et al., Reference Costa, Pinto, Morais, Oliveira and Barreto2017) and bony seed coats as in Psidium (Landrum and Stevenson, Reference Landrum and Stevenson1986)] have been suggested as new adaptive advantages associated with the increased rates of speciation of fleshy-fruited species.

Eugenia (Myrteae) with 1218 species (POWO) is the largest genus of Myrtaceae in the Neotropics (Mazine et al., Reference Mazine, Faria, Giaretta, Vasconcelos, Forest and Luca2018). After the ancestors of Eugenia migrated to southern South America, there was species diversification and dispersal to northern South America and the Caribbean region. The highest numbers of Eugenia species in South America are in the Atlantic Forest, Amazon Forest and Cerrado (Brazilian savanna) with 250, 91 and 74 species, respectively (Bünger et al., Reference Bünger, Mazine, Forest, Bueno, Stehmann and Lucas2016). For E. uniflora, there are two evolutionary lineages in the Atlantic Forest, one in the north and another in the south (Turchetto-Zolet et al., Reference Turchetto-Zolet, Salgueiro, Turchetto, Cruz, Veto, Garros, Segatto, Freitas and Margis2016). Eugenia was dispersed from South America to Southeast Asia and Africa (van der Merwe et al., Reference van der Merwe, van Wyk and Botha2005; Lucas et al., Reference Lucas, Harris, Mazine, Belsham, Nic Lughadha, Telford, Gasson and Chanse2007; Mazine et al., Reference Mazine, Faria, Giaretta, Vasconcelos, Forest and Luca2018). Two clades of Eugenia occur in southern Africa: one related to New World Eugenia and one related to Old World Eugenia (van der Merwe et al., Reference van der Merwe, van Wyk and Botha2005).

Using chloroplast and nuclear DNA sequences of the genus Myrceugenia (Myrteae), Murillo-A et al. (Reference Murillo-A, Stuessy and Ruiz2016) determined that four lineages of the genus had diverged in South America by the early Miocene: three in Chile and one in southeastern Brazil. One Chilean lineage dispersed northward, and species became part of the subtropical montane flora; part of this lineage subsequently migrated southward. The other two Chilean lineages migrated south, and species became part of the cool-temperate rainy forest flora. The lineage in southeast Brazil diversified, with species now growing in the Paraná (Araucaria angustifolia) forest, tropical semi-deciduous forests, pampas and Cerrado.

Myrcia (Myrteae) is a large genus with c. 800 species, and it is divided into nine sections (Lima et al., Reference Lima, Goldenberg, Forest, Cowan and Lucas2021). Santos et al. (Reference Santos, Lucas, Sano, Buerki, Staggemeier and Forest2017) concluded that Myrcia originated in the Montane Atlantic Forest of eastern Brazil in the late Eocene to early Miocene, after which some lineages diversified in the region. Other lineages migrated northward to the Amazon, Guyana and Caribbean regions, where diversification occurred. Also, lineages of Myrcia dispersed from the Atlantic Forest to regions with Cerrado, Yungas (subtropical cloud forest) and savanna vegetation, which was followed by diversification of new species (Amorim et al., Reference Amorim, Vasconcelos, Souza, Alves, Antonelli and Lucas2019). In fact, Myrcia section Aguava seems to have originated in the Cerrado in the mid-Miocene (Lima et al., Reference Lima, Goldenberg, Forest, Cowan and Lucas2021).

Syzygium (Syzygieae) with 1231 species (POWO) is an Old World tropical/subtropical genus of trees or rarely shrubs, many of which are cultivated for their edible fleshy fruits (Uddin et al., Reference Uddin, Hossain, Reza, Nasrin and Alam2022). Using data from molecular phylogenetic studies of Syzygium, Low et al. (Reference Low, Rajaraman, Tomlin, Ahmad, Ardi, Armstrong, Athen, Berhaman, Bone, Cheek, Cho, Choo, Cowie, Crayn, Fleck, Ford, Forster, Girmansyah, Goyder and Gray2022) determined that the genus originated in Sahul, which was a land mass consisting of Australia, New Guinea and the Aru Islands that was connected due to low seas levels during the Last Glacial Maximum, e.g. c. 23,000–19,000 years ago (Clark and Mix, Reference Clark and Mix2002). Migration of Syzygium from Sahul to the Sunda Islands (Brunei, East Timor, Indonesia, Malaysia and Singapore) has occurred at least 12 times, and each dispersal event was followed by species diversification. Dispersal and diversification have resulted in various species of Syzygium growing in the Northern Pacific, India and Africa (Low et al., Reference Low, Rajaraman, Tomlin, Ahmad, Ardi, Armstrong, Athen, Berhaman, Bone, Cheek, Cho, Choo, Cowie, Crayn, Fleck, Ford, Forster, Girmansyah, Goyder and Gray2022). These authors note that dispersal to a new region often has resulted in rapid speciation.

Background information on reproductive biology

Apomixis, polyploidy and polyembryony

The basic haploid chromosome number for the Myrtaceae is n = 11, and ‘… the vast majority of species are diploid with 2n = 22 …’, e.g. Eucalyptus spp. (Grattapaglia et al., Reference Grattapaglia, Vaillancourt, Shepherd, Thumma, Foley, Külheim, Potts and Myburg2012). However, there are triploid and tetraploid species of Myrtaceae (Costa and Forni-Martins, Reference Costa and Forni-Martins2007). Polyploidy is frequent in fleshy-fruited genera such as Eugenia, Myrcia, Psidium (Costa and Forni-Martins, Reference Costa and Forni-Martins2007; Neto et al., Reference Neto, Santos, Lucas, Veto, Barrientos-Diaz, Staggemeier, Vasconcelos and Turchetto-Zolet2022) and Syzygium (Ouadi et al., Reference Ouadi, Sierro, Kessler and Ivanov2023). Neto et al. (Reference Neto, Santos, Lucas, Veto, Barrientos-Diaz, Staggemeier, Vasconcelos and Turchetto-Zolet2022) concluded that hybridization and allopolyploidy have contributed to speciation in the Myrteae. Further, Silveira et al. (Reference Silveira, Machado, Forni-Martins, Verola and Costa2016) found that polyploid individuals of Eugenia species grew in habitats with more adverse environmental conditions than diploid individuals.

Apomixis (agamospermy) has been reported for several species of Myrtaceae, and in Syzygium cumini, S. jambos and S. paniculatum asexual embryos are derived from the ovules, either the integuments or nucellus (Souza-Pérez and Speroni, Reference Souza-Pérez and Speroni2017), i.e. adventitious embryony or sporophytic apomixis (van der Pijl, Reference Van der Pijl1934; Gustafsson, Reference Gustafsson1947). In S. jambos, up to 13 embryos have been found in a seed (van der Pijl, Reference Van der Pijl1934), and, in S. cumini, the number of embryos in a seed ranges from 1 to 7 (Rekha et al., Reference Rekha, Talang and Sane2020). In Psidium cattleianum, however, the asexual embryos are of diplosporic origin, i.e. the megaspore mother cell forms an embryo sac (Souza-Pérez and Speroni, Reference Souza-Pérez and Speroni2017).

In some cases, both asexual (adventitious embryony) and sexual embryos are formed in the same seed (i.e. polyembryony of Ganeshaiah et al. (Reference Ganeshaiah, Shaanker and Joshi1991)), and they are in close proximity to each other (Koltunow, Reference Koltunow1993). In seeds of Syzygium paniculatum (a rare polyploid rainforest tree in Australia) with two embryos, the sexual embryo is larger than the asexual one (Thurlby et al., Reference Thurlby, Wilson, Sherwin, Connelly and Rossetto2012). However, if seeds of S. paniculatum have more than two embryos, the sexual embryo is not the largest one. The largest embryo in a seed (be it sexual or asexual) produces the largest seedling. Ganeshaiah et al. (Reference Ganeshaiah, Shaanker and Joshi1991) concluded that ‘… polyembryony is a maternal counter strategy to compensate for the loss in her fitness due to brood reduction caused by sibling rivalry’.

Flowering of fleshy-fruited species

The flowering season often begins with the onset of the rainy season, e.g. in Australia (Shapcott, Reference Shapcott1998), Brazil (Torezan-Silingardi and Oliveira, Reference Torezan-Silingardi and Oliveira2004; Staggemeier et al., Reference Staggemeier, Diniz-Filho and Morellato2010; Vogado et al., Reference Vogado, Camargo, Locosselli and Morellato2016) and Venezuela (Zapata and Arroyo, Reference Zapata and Arroyo1978). Rhodomyrtus tomentosa grows in a subtropical monsoon climate in China and flowers in spring, which is at or near the beginning of the summer wet season (Wei et al., Reference Wei, Chen, Ren and Yin2009). On Chiloé Island (Chile), the flowering of 13 species of Myrtaceae mostly occurred in summer, at which time the mean maximum temperature was 17.6°C (Smith-Ramírez et al., Reference Smith-Ramírez, Armesto and Figueroa1998). Syzygium alternifolium grows in tropical deciduous forests in India and flowers in the dry season (late winter and early spring) when temperatures are relatively low (Raju et al., Reference Raju, Krishna and Chandra2014). Many species of Eugenia in South Africa flower in spring, but a few species flower in early summer; E. verdoorniae flowers in winter (Van Wyk and Lowrey, Reference Van Wyk and Lowrey1988). Drought can delay flowering causing some Eugenia species not to flower for one or more seasons. In the case of the rhizomatous E. albanensis, grassland fires promoted flowering (Van Wyk and Lowrey, Reference Van Wyk and Lowrey1988).

In the Atlantic Forest of eastern Brazil, 24 of 34 (70%) species of Myrtaceae flowered during the wet season; however, fruits were available for animals all year. At least one species of Myrtaceae had ripe fruits each month of the year, but, in some months, six or more species had ripe fruits (Staggemeier et al., Reference Staggemeier, Diniz-Filho and Morellato2010). Although most of the 13 taxa of Myrtaceae studied on Chiloé Island (Chile) flowered in summer, the duration of flowering varied from 2 to 5 months with a mean flowering time of 3.0 months (Smith-Ramírez et al., Reference Smith-Ramírez, Armesto and Figueroa1998). Further, one or more taxa had ripe fruits in each month of the year. In the sandy coastal plain in southeastern Brazil, at least one species of Myrtaceae also had ripe fruit at all times of the year (Oliveira et al., Reference Oliveira, Benevides, Greco, LeãoL, Rodarte and Lima2022).

Mass flowering occurs in various species of fleshy-fruited Myrtaceae, e.g. Eugenia spp. (Silva and Pinheiro, Reference Silva and Pinheiro2009), Syzygium alternifolium (Raju et al., Reference Raju, Krishna and Chandra2014), S. nervosum (Shapcott, Reference Shapcott1998) and S. tierneyanum (Hopper, Reference Hopper1980). Proença and Gibbs (Reference Proença and Gibbs1994) found four flowering strategies among eight sympatric species of Myrtaceae in central Brazil: big bang, synchronized mass flowering that is completed in about 1 week; pulsed-bang, synchronized flowering for about 1 week but with intervals of up to several days when no flowers open; cornucopia, many flowers produced per plant over a period of about 1 month and steady state, plants produce only a few flowers each day for about 1 month. Torezan-Silingardi and Oliveira (Reference Torezan-Silingardi and Oliveira2004) found that plants of Myrcia rostrata flowered in pulses over a period of 13 weeks with many or a few flowers opening each day. Since flowering in the M. rostrata population was not well synchronized, this seems to be a modified steady-state pattern of flowering. Plants of M. tomentosa had a pulsed-bang flowering strategy with three synchronized flowering events each year.

Flowering of dry-fruited species

In Australia, most capsular-fruited species of Myrtaceae flower in spring, e.g. Eucalyptus (Birtchnell and Gibson, Reference Birtchnell and Gibson2006), Leptospermum and Melaleuca (Beardsell et al., Reference Beardsell, O'Brien, Williams, Knox and Calder1993), presumably in response to increased day length and/or temperature (Beardsell et al., Reference Beardsell, O'Brien, Williams, Knox and Calder1993). However, the flowering of Chamelaucium uncinatum is promoted by short days and temperatures of 20–25°C resulting in flowering during winter (Dawson and King, Reference Dawson and King1993). In Victoria (Australia), the commencement of flowering for 28 species of Eucalyptus ranged from late winter to mid-autumn (Birtchnell and Gibson, Reference Birtchnell and Gibson2006). The duration of the flowering period of these 28 species ranged between 1 and 8 months; thus, pollinators (e.g. bees) had a continuous supply of Eucalyptus flowers to visit throughout the year. The flowering frequencies of the 28 species were 1–7 years, but most species flowered every 2–4 years. Even in off-years for flowering of a species, a few individuals produced flowers.

Franklin et al. (Reference Franklin, Barnes and Winlaw2016) investigated the mass flowering of Eucalyptus mediocris in dry sclerophyll forests in northern Queensland (Australia). Trees flowered from late autumn to late summer, and most (75%) of them flowered heavily. Mass synchronized flowering occurred about once each decade, i.e. flowering occurred at irregular intervals with high seed production following each flowering event (masting). In contrast to E. mediocris, Metrosideros excelsa flowered profusely for about 2 weeks in summer (Schmidt-Adam et al., Reference Schmidt-Adam, Gould and Murray1999, Reference Schmidt-Adam, Young and Murray2000), which was a big bang flowering strategy.

Pollinators of fleshy-fruited species

Flowers of fleshy-fruited species are pollinated by a diversity of organisms, and the reward for visitors may be nectar and/or pollen. If nectar is the reward, anthers and/or pollen grains smell sweet, e.g. Eugenia (VanWyk and Lowrey, Reference Van Wyk and Lowrey1988). Eugenia flowers are pollinated by insects, in particular bees (Hymenoptera) including the honeybee Apis mellifera (Zapata and Arroyo, Reference Zapata and Arroyo1978; Van Wyk and Lowrey, Reference Van Wyk and Lowrey1988; Silva and Pinheiro, Reference Silva and Pinheiro2009). Coleoptera and Diptera also visit the flowers of Eugenia (Silva and Pinheiro, Reference Silva and Pinheiro2009). In central Brazil, flowers of Blepharocalyx salicifolia, Campomanesia pubescens, C. velutina, Eugenia dysenterica, Myrcia linearifolia, M. rhodosepala (Proença and Gibbs, Reference Proença and Gibbs1994), M. rostrata, M. tomentosa (Torezan-Silingardi and Oliveira, Reference Torezan-Silingardi and Oliveira2004), Psidium firum and Siphoneugena densiflora (Proença and Gibbs, Reference Proença and Gibbs1994) have a sweet odour but no nectar, and pollen is the reward for flower visitors, which are various species of bees.

Fleshy-fruited species such as Eugenia speciosa, Gomidesia schaueriana, Myrcia multiflora, M. racemosa, M. splendens and Psidium cattleianum growing in the coastal plain forest of São Paulo state in Brazil begin to flower during the onset of the rainy season in spring (September–October) (Fidalgo and Kleinert, Reference Fidalgo and Kleinert2009). Flowers mainly were visited by bees, which either touched the anthers or buzzed (sonicated) them to collect pollen. The breeding system for E. speciosa, G. schaueriana, M. racemosa and M. splendens was xenogamy (required cross-pollination) and that of M. multiflora and P. cattleianum facultative xenogamy, i.e. adapted for cross-pollination by insects but if pollinators are not present selfing occurs.

Twelve of 16 species of insects (Apidae) that visited flowers of Rhodomyrtus tomentosa growing in southeastern China had pollen grains on their bodies, which became attached to the stigma when bees were allowed to visit virgin flowers (Wei et al., Reference Wei, Chen, Ren and Yin2009). Pollen is the reward for insects visiting the flowers of R. tomentosa. The bees Amegilla florea and Xylocopa nasalis were the primary visitors/pollinators, and females were observed collecting pollen into the pollen basket on their hind legs.

Syzygium species have both pollen and nectar as rewards for pollinators, and flowers are visited by many insects. For example, in the southern Eastern Ghats of India, flowers of S. alternifolium were visited by 32 species of insects, including bees, beetles, butterflies, flies, hawkmoths and wasps, and by the African fat-tailed gecko (Hemitheconyx caudicinctus). All flower visitors collected nectar, while the bee Trigona iridipennis collected both nectar and pollen (Raju et al., Reference Raju, Krishna and Chandra2014). In Zambia, Hymenoptera, Diptera, Coleoptera and Lepidoptera visited flowers of S. guineense, and nectar-collecting was the most common behaviour observed (Coppinger and Stanley, Reference Coppinger and Stanley2023). Apis mellifera was the most frequent flower visitor followed by Braunsapis bees, wasps and Diptera. Among the various invertebrate visitors to flowers of S. cormiflorum in the Australian rainforest, only the bodies of moths, ants, cockroaches, mites and a Staphylinid beetle had pollen on them (Crome and Irvine, Reference Crome and Irvine1986). In addition, four species of honeyeater birds (Meliphagidae) and two species of small blossom bats (Pteropodidae) were daily visitors of S. cormiflorum flowers; bats visited after dusk and before dawn. Flowers of S. tierneyanum, a species of northern Australian rainforests, were visited by 45 species of animals: bats, birds, bees (Apis mellifera), butterflies, hawkmoths and four other kinds of moths and honeyeaters (Hopper, Reference Hopper1980). Hawkmoths and honeyeaters were the most frequent native pollinators, and nectar was the reward for flower visitors. In the bird-pollinated flowers of Acca sellowiana and Myrrhinium atropurpureum, the reward is fleshy, sweet petals (Gressler et al., Reference Gressler, Pizo and Morellato2006).

Pollination of dry-fruited species

Pollinators include insects such as ants, bees, beetles, butterflies, flies, moths and wasps and vertebrates such as bats, birds and small marsupials (Beardsell et al., Reference Beardsell, O'Brien, Williams, Knox and Calder1993; Carthew and Goldingay, Reference Carthew and Goldingay1997; Yates et al., Reference Yates, Hopper and Taplin2005; Sharanya et al., Reference Sharanya, Aswani and Sabu2014; Groom and Lamont, Reference Groom and Lamont2015; Chauhan et al., Reference Chauhan, Chauhan and Galetto2017). For Australian genera such as Callistemon, Eucalyptus and Melaleuca, bees, especially those in the family Colletidae, are important pollinators, and they collect both pollen and nectar (Beardsell et al., Reference Beardsell, O'Brien, Williams, Knox and Calder1993). However, the honeybee (Apis mellifera) is sometimes the most common pollinator (Yates et al., Reference Yates, Hopper and Taplin2005).

Bird pollinators include various species of honeyeaters, lorikeets (Ford et al., Reference Ford, Paton and Forde1979), honeycreepers (Carpenter, Reference Carpenter1976), sunbirds, parrots and oriental white-eyed sparrows (Chauhan et al., Reference Chauhan, Chauhan and Galetto2017). Phillips et al. (Reference Phillips, Hopper and Dixon2010) concluded that bird pollination results in the movement of pollen for relatively long distances and could help reduce inbreeding compared with insect pollination. However, there was no significant difference in the fruit set of honeyeater-pollinated flowers of Calothamnus quadrifus growing in large versus small fragments of Kwongan Sand Plain (Mediterranean) shrubland in south-west Australia (Yates et al., Reference Yates, Elliott, Byrne, Coates and Fairman2007). Also, seed germination, seedling development and seedling mortality did not increase significantly with increased fragment size; mean seed germination across all population sizes ranged between 78 and 100%. However, the authors concluded that bird movement of pollen between population fragments would not prevent inbreeding depression from occurring in small fragments. Bats are also long-distance pollinators, and they can deposit large amounts of pollen with a variety of genotypes on flower stigmas (Fleming et al., Reference Fleming, Geiselman and Kress2009).

Breeding systems

Self-compatibility versus self-incompatibility is one of the first considerations in understanding the breeding system of a species, and many hand cross- and hand self-pollination experiments have been done with Myrtaceae. Much variation in self-compatibility and self-incompatibility is found in the Myrtaceae. Some species of Eugenia are self-compatible, but others are self-incompatible (Proença and Gibbs, Reference Proença and Gibbs1994; Silva and Pinheiro, Reference Silva and Pinheiro2009). Blepharocalyx salicifolius, Campomanesia velutina and Siphoneugenia densiflora are strictly self-incompatible; Myrcia linearifolia and C. pubescens mostly self-incompatible but with low selfing; and Eucalyptus argutifolia (Kennington and James, Reference Kennington and James1997), Eugenia dysenterica, M. rhodosepala, Psidium firmum, Syzygium guineense (Coppinger and Stanley, Reference Coppinger and Stanley2023) and S. nervosum (Shapcott, Reference Shapcott1998) self-compatible (Proença and Gibbs, Reference Proença and Gibbs1994). Kunzea pomifera is mostly self-compatible, and one barrier to self-fertilization is that pollen tubes do not grow into the ovules (Page et al., Reference Page, Moore, Will and Halloran2010). Not only is E. argutifolia self-compatible, but Kennington and James (Reference Kennington and James1997) concluded that geitonogamous pollination (i.e. pollen from other flowers on the same plant) was probably more common than outcrossing. High seed abortion in the late stages of development prevents the occurrence of high homozygosity in the population.

Some trees of Metrosideros excelsa are self-compatible and others self-incompatible (Schmidt-Adam et al., Reference Schmidt-Adam, Gould and Murray1999). Seed germination was 98.4% for fertile seeds of M. excelsa from all pollination treatments; thus, no inbreeding depression was detected. In Hawaii (USA), flowers on red-flowered trees of M. collina are partly self-incompatible, but those on yellow-flowered trees are totally self-compatible (Carpenter, Reference Carpenter1976). In New Zealand, the endangered M. bartletti is self-incompatible and cross-pollination is required for seed set (van der Walt et al., Reference van der Walt, Burritt and Nadarajan2022).

Fruit set and seed formation in Myrcianthus coquimbensis did not differ significantly between outcrossed and selfed flowers (García-Guzmán et al., Reference García-Guzmán, Loayza and Squeo2020). The germination of seeds from outcrossed, selfed and control flowers of Myrtus communis was 79, 52 and 45%, respectively, i.e. no inbreeding depression (González-Varo and Traveset, Reference González-Varo and Traveset2010). These authors found that outcrossing enhanced the number of seeds per fruit, seed germination and seedling growth, but it did not enhance fruit set. Furthermore, the authors acknowledged that their sample size of 10 mother plants is very modest with low statistical power, and one of the main conclusions is that pollen limitation may be genotype-dependent. However, the mass of seeds from selfed flowers of M. communis was significantly higher than that of seeds from outcrossed flowers, suggesting a trade-off between seed number and mean seed mass within a fruit.

Fruit set for flowers of Campomanesia pubescens that were bagged, hand self-pollinated, cross-pollinated or nonbagged (natural pollination) was 0, 40.3, 65.7 and 17.8%, respectively, and germination was 0, 78.5, 100.0 and 87.7%, respectively (Rodrigues et al., Reference Rodrigues, Fidalgo and Barbedo2017). Seeds from hand cross-pollinated flowers had faster germination and seedling growth than those from hand self-pollinated flowers. Fruit set for flowers of Eugenia uniflora that were bagged, hand self-pollinated, and cross-pollinated or nonbagged/natural pollination was c. 15.5, 11.1, 34.4 and 52.0%, respectively, and germination was 93.6, 98.5, 94.6 and 91.6%, respectively (Fidalgo et al., Reference Fidalgo, Cécel, Mazzi and Barbedo2019). That is, there was no inbreeding depression for seed germination. The average germination per gram of seeds (plus chaff) was 280 and 327 for seeds from self- and cross-pollinated flowers of Eucalyptus regnans, respectively (Eldridge and Griffin, Reference Eldridge and Griffin1983). Compared with outcrossing, self-pollination significantly decreased the seed set of E. globulus subsp. globulus, but there was no effect on seed germination percentage or rate (Hardner and Potts, Reference Hardner and Potts1995).

Self-pollinated flowers of Syzygium rubicundum had c. 2.1% fruit set, and as the crossing distance increased to 1–2 km fruit set increased to c. 9.5% (Stacy, Reference Stacy2001). However, an increase in crossing distance up to 12 km decreased fruit set to c. 3%. Regardless of crossing distance, seed germination percentages were not significantly affected, while cumulative fitness was similar to fruit set. A pollen donor from a close-neighbor tree resulted in biparental inbreeding depression, but that from trees in separate/distant forests resulted in outbreeding depression.

Some species in various genera of Myrtaceae have male and hermaphroditic flowers on the same plant (andromonoecy), including Beaufortia, Conothamnus, Eucalyptus, Leptospermum, Melaleuca, Phymatocarpus and Regelia (Carr et al., Reference Carr, Carr and Ross1971; Primack and Lloyd, Reference Primack and Lloyd1980; Beardsell et al., Reference Beardsell, O'Brien, Williams, Knox and Calder1993). Other breeding systems reported for species of Myrtaceae include dioecy and gynodioecy. Dioecious species have male and female flowers on different individual plants, e.g. Myrcia almasensis (Nic Lughadha, Reference Nic Lughadha1994), and the most common pollinators are small bees (Bawa, Reference Bawa1980). Dioecy is rare among angiosperms, but it has been reported in the Myrtaceae (Landrum, Reference Landrum1986; Nic Lughadha, Reference Nic Lughadha1994; Renner, Reference Renner2014; Käfer et al., Reference Käfer, Marais and Pannell2017), e.g. Pimenta guatemalensis (Landrum, Reference Landrum1986). Cryptic dioecy also occurs in the Myrtaceae (Chapman, Reference Chapman1964; Van Wyk and Lowrey, Reference Van Wyk and Lowrey1988; Nic Lughadha and Proença, Reference Nic Lughadha and Proença1996). For example, populations of about 15 species of Eugenia native to South Africa consist of plants that are either male or have hermaphroditic flowers (androdioecious), but these plants are functionally dioecious (Van Wyk and Lowrey, Reference Van Wyk and Lowrey1988). Fruits are formed only when hermaphroditic flowers are pollinated with pollen from male flowers because pollen from hermaphroditic flowers is not viable.

Gynodioecious species have only female (male sterile) flowers on some plants and hermaphroditic flowers on other plants in the same population. The ratio of female and hermaphroditic flowers can vary greatly within and among populations. Gynodioecy occurs in only about 2% of the angiosperm genera, but it is taxonomically widespread and occurs in eumagnoliids, monocots and eudicots (Dufay et al., Reference Dufay, Käfer, Henry, Mousset and Marais2014; Baskin and Baskin, Reference Baskin and Baskin2020). The Myrtaceae is 1 of 81 families with this kind of breeding system (Dufay et al., Reference Dufay, Käfer, Henry, Mousset and Marais2014). However, the only example of a gynodioecious Myrtaceae that we have found in the literature is Eucalyptus leucoxylon subsp. leucoxylon (Ellis and Sedgley, Reference Ellis and Sedgley1993). In this taxon, some trees in the population have female flowers and others have hermaphroditic flowers. Anthers in the hermaphroditic flowers dehisced before the flowers opened resulting in c. 93% of the pollen being deposited on the stigma; the other 7% of the pollen was available for cross-pollination. Female flowers were cross-pollinated. However, there was no difference in seed set from cross-pollination for the two flower morphs.

Seed dispersal

Fleshy fruits of Myrtaceae are eaten by various animals, including birds, bats, carnivorous mammals, lemurs, monkeys, rodents, marsupials and ungulates (Dew and Wright, Reference Dew and Wright1998; Pizo, Reference Pizo, Levey, Silva and Galetti2002, Reference Pizo2003; Côrtes et al., Reference Côrtes, Cazetta, Staggemeier and Galetti2009; Sinu et al., Reference Sinu, Shivanna and Kuriakosw2012; Tang et al., Reference Tang, Xu, Glanders, Ding, Ma, Sheng and Cao2012; Lessa et al., Reference Lessa, Geise and Costa2013; Chaves et al., Reference Chaves, Bicca-Marques and Chapman2018). Seed dispersal of Myrtaceae in the Atlantic Forest of Brazil included birds (dispersing 14 Myrtaceae genera), bats (2), carnivorous mammals (6), monkeys (9), rodents (1), marsupials (2) and ungulates (2) (Pizo, Reference Pizo, Levey, Silva and Galetti2002). Nine of the 14 genera had only one to two seed disperser(s), while Campomanesia, Eugenia, Myrcia, Myrciaria and Psidium had 4, 5, 3, 3 and 6 dispersers, respectively.

Many species of birds eat fleshy fruits of Myrtaceae and then disperse the seeds (Pizo, Reference Pizo, Levey, Silva and Galetti2002, Reference Pizo2003; Bollen et al., Reference Bollen, Van Elsacker and Ganzhorn2004; Côrtes et al., Reference Côrtes, Cazetta, Staggemeier and Galetti2009; Sinu et al., Reference Sinu, Shivanna and Kuriakosw2012; Hicks and Elliott, Reference Hicks and Elliott2020). Birds differ in their fruit-eating behaviour: (1) swallow the whole fruit, (2) roll the fruit around in the mouth and spit out the seeds and (3) eat some of the fruit while leaving the seed attached to the parent plant (Sinu et al., Reference Sinu, Shivanna and Kuriakosw2012). Only birds that swallow the fruit and defecate or regurgitate the seeds at sites away from the parent plant are effective seed dispersers. For example, in the Atlantic Forest of Brazil, 17 species of birds visited fruits of Eugenia umbelliflora, but only Turdua amaurochalinus and T. rufiventris had the highest probability (0.28 and 0.24, respectively) of dispersing seeds (Côrtes et al., Reference Côrtes, Cazetta, Staggemeier and Galetti2009). The crab-eating fox (Cerdocyon thous) is a secondary disperser of E. umbelliflora seeds initially dispersed by birds and then dropped to the soil surface (Cazetta and Galetti, Reference Cazetta and Galetti2009). Germination percentage was not increased by gut passage through the fox, but germination speed was increased significantly.

In the Atlantic Forest of Brazil, bats eat the fruits of Eugenia stictosepala, Psidium catleianum and P. guajava and disperse the seeds (Pizo, Reference Pizo, Levey, Silva and Galetti2002). The bat species Cynopterus sphinx and Rousettus leschenault removed fruits from Syzygium oblatum trees growing in Yunnan Province, China, and carried them for up to 73 m away from the parent trees (Tang et al., Reference Tang, Xu, Glanders, Ding, Ma, Sheng and Cao2012). Seedling survival of S. oblatum under parent trees, in forest gap and under feeding-roost trees was 78.3, 91.7 and 86.7%, respectively. The carnivorous mammals coatis and canids and the ungulates tapirs and deer in the Atlantic Forest eat fruits of Myrtaceae that have fallen on the ground (Pizo, Reference Pizo, Levey, Silva and Galetti2002). The rodents agoutis (Dasyprocta) and spiny rats (Echimyidae) also collect fleshy fruits of Myrtaceae from the soil surface, and they may cache some of them in soil/litter up to 6.1 m away from the fruiting trees (Pizo, Reference Pizo, Levey, Silva and Galetti2002).

Monkeys eat fleshy fruits of various species of Myrtaceae. Brown howler monkeys are legitimate seed dispersers of Myrtaceae and other plant families with fleshy fruits that grow in their habitat (Chaves et al., Reference Chaves, Bicca-Marques and Chapman2018). Monkeys swallow the fruits and later defecate seeds in new locations away from the parent trees. Monkeys defecate seeds in groups, while birds may drop individual seeds (Pizo, Reference Pizo2003). A comparison of seedling survival for clumped versus individual seeds in the seed-deposition site revealed that the isolated seeds of Gomidesia anacardiifolia and Marlierea obscura (i.e. bird-dispersed seeds) had higher survival than clumped seeds. Marsupials in particular didelphids eat fleshy fruits of angiosperms, including those of Myrtaceae (Lessa et al., Reference Lessa, Geise and Costa2013). After gut passage, seeds of Myrcia sp. germinated to higher percentages than control seeds, while those of Psidium sp. germinated to a lower percentage than control seeds (Lessa et al., Reference Lessa, Geise and Costa2013).

The fleshy fruits of Myrtus communis in the Mediterranean shrublands of southern Europe are dispersed by birds (Herrera, Reference Herrera1995; Traveset et al., Reference Traveset, Riera and Mas2001) and the carnivorous mammals red fox and pine marten (Aronne and Russo, Reference Aronne and Russo1997; Traveset et al., Reference Traveset, Riera and Mas2001). Also, seeds of M. communis have an elaiosome (fleshy body on seed that is rich in lipids and proteins) and are dispersed by ants (Aronne and Wilcock, Reference Aronne and Wilcock1994).

After dry fruits of Myrtaceae, e.g. Calothamnus, Corymbia, Eucalyptus and Melaleuca, open and release seeds and indehiscent fruits, e.g. Calytrix, Darwinia and Micromyrtus, fall from the parent plant, both gravity and wind facilitate dispersal. Fruits of Calytrix retain the calyx, which promotes dispersal by wind (Groom and Lamont, Reference Groom and Lamont2015). Seeds of Metrosideros polymorpha are dispersed by wind and can reach seed densities of 363, 137, 37, 25 and 20 m−2 at distances of 25, 50, 100, 150 and 250 m, respectively, beyond the edge of the forest (Drake, Reference Drake1992).

Following the dispersal of seeds/fruits via gravity and wind, ants may take them and thus serve as secondary dispersers (e.g. Andersen and Ashton, Reference Andersen and Ashton1985; Myerscough, Reference Myerscough1998). After the fruits of Corymbia torelliana open, c. 88% of the seeds are dispersed by gravity, but a few seeds in each fruit are embedded in resin in the open fruits and are not dispersed (Wallace et al., Reference Wallace, Howell and Lee2008). Stingless bees in the genus Trigona collect the resin, and as they do so they collect seeds of C. torelliana. Bees carry the seeds and resin to their nests 20–220 m away from the parent trees, after which they discard the seeds from their nests; these seeds germinate to about 95%.

It should be noted that the seeds of Myrtaceae taken by ants, beetles, birds, lemurs, lygaeid bugs, monkeys, rodents and other animals may serve as food for the animals, i.e. seed predation (Ashton and Frankenberg, Reference Ashton and Frankenberg1979; Ashton, Reference Ashton1979; Andersen and Ashton, Reference Andersen and Ashton1985; Wellington and Noble, Reference Wellington and Noble1985; Dew and Wright, Reference Dew and Wright1998; Silva and Pinheiro, Reference Silva and Pinheiro2009; Carvalho and Pizo, Reference Carvalho and Pizo2023). For example, no seeds of Eucalyptus regnans were found in/on the soil in mature forests of this species, although seed rain/fall was good each year (Ashton, Reference Ashton1979). Seeds were eaten/destroyed by several species of ants including Chelaner leae, Prolasius frunneas, P. flavicorns and P. pallidus. After a fire, however, massive seed fall from canopy-stored seeds not only satiated the ants, but there was ‘a temporary interference of ant foraging activity’. In southeastern Australia, the number of viable seeds in the annual seed rain of Eucalyptus baxteri, Leptospermum juniperinum and L. myrsinoides was 13, 480 and 800 seeds m−2 yr−1, respectively, but the number of seeds remaining after predation was 1.3, 48 and 80 m−2 yr−1, respectively (Andersen, Reference Andersen1989).

Kinds of embryos in seeds of Myrtaceae

Martin (Reference Martin1946) listed bent, folded and linear embryos for Myrtaceae, but investing and spatulate embryos also occur in this family (e.g. Dawson, Reference Dawson1970; Landrum and Kawasaki, Reference Landrum and Kawasaki1997; Wilson, Reference Wilson and Kubitzki2010). Thus, five morphologically distinct kinds of embryos are found in Myrtaceae (Fig. 1). A linear-full embryo (i.e. a fully developed linear embryo) is long, usually curved with small, recurved cotyledons and an enlarged hypocotyl that is greatly swollen in some species (Fig. 1A). A spatulate embryo has spoon-shaped cotyledons attached directly above a straight (easily visible) hypocotyl/radicle (Fig. 1B). A bent embryo has rounded cotyledons and a hypocotyl that curves sharply around the end of the cotyledons (Fig. 1C). A folded embryo has large foliaceous cotyledons that are folded together and an obviously protruding hypocotyl that may be somewhat curved (Fig. 1D). An investing embryo has thick fleshy cotyledons that cover most, or all, of the embryo axis (Fig. 1E). The investing embryo of Myrtaceae has been described as massive but undivided, i.e. undifferentiated (McVaugh, Reference McVaugh1956). However, Justo et al. (Reference Justo, Alvarenga, Alves, Guimarães and Strassburg2007) clearly showed that the investing embryo of Eugenia pyriformis was differentiated and had an embryo axis c. 1.0 mm in length located between the cotyledons.

Figure 1. Embryo types of Myrtaceae. (A) Linear-full (myrtoid); (B) spatulate; (C) bent; (D) folded (myrcioid) and (E) investing (eugenioid). A, axis (which is covered by cotyledons); C, cotyledons; H, hypocotyl.

Investing, folded and linear-full embryos in tribe Myrteae have been called eugenioid, myrcioid and myrtoid embryos, respectively (e.g. Landrum and Stevenson, Reference Landrum and Stevenson1986; Lucas et al., Reference Lucas, Harris, Mazine, Belsham, Nic Lughadha, Telford, Gasson and Chanse2007; da Silva and Mazine, Reference da Silva and Mazine2016). However, in this review, we refer to all embryos using the embryo classification system of Martin (Reference Martin1946) as modified by Baskin and Baskin (Reference Baskin and Baskin2007).

In seeds of Myrtaceae with a bent, folded, investing or linear-full embryo, there is a shoot apical meristem between the cotyledons and a root apical meristem at the lower end of the hypocotyl. The hypocotyl is the first structure to emerge from seeds with a bent, folded, investing and linear-full embryo (see spatulate embryo below), after which the primary root and a shoot are produced by the apical meristems (Beltrati, Reference Beltrati1978; Landrum and Stevenson, Reference Landrum and Stevenson1986; Aronne and de Micco, Reference Aronne and de Micco2004; Meza and Bautista, Reference Meza and Bautista2007; Rego et al., Reference Rego, Cosmo, Gogosz, Kuniyoshi and Nogueira2011; Bardales et al., Reference Bardales, Pisco, Flores, Mashacuri, Ruíz, Correa and Gómez2014; Cosmo et al., Reference Cosmo, Gogosz, Rego, Nogueira and Kuniyoshi2017; Freitas et al., Reference Freitas, de Lucena, Bonilla, da Silva and Sampaio2018). The amount (length) that the hypocotyl extends from seeds before the primary root is visible varies, resulting in some seedlings with a relatively long hypocotyl (between the seed and root) (Aronne and de Micco, Reference Aronne and de Micco2004) and others with a short hypocotyl (Beltrati, Reference Beltrati1978; Nacata and Andrade, Reference Nacata and Andrade2020). This kind of seed dormancy was placed in Subclass 4 (Hypocotylar) of Class physiological dormancy (PD) by Baskin and Baskin (Reference Baskin and Baskin2021). The dormancy formula they suggested for seeds is $C_{xb}^{{m}^{\prime}}$, where C is class physiological dormancy (PD), × level 1 (nondeep), 2 (intermediate) or 3 (deep) of PD, subscript b that warm temperatures are required to break PD and superscript m′ that the root and shoot arise from meristematic tissue on opposite ends of the hypocotyl after the hypocotyl has emerged from the seed. For nondormant (ND) seeds, the formula is $C_{{\rm nd}}^{{m}^{\prime}}$, where subscript nd means nondormant (Baskin and Baskin, Reference Baskin and Baskin2021).

Information about the germination morphology of seeds with a spatulate embryo is not clear. Some authors (e.g. Ladiges et al., Reference Ladiges, Foord and Willis1981; Robinson et al., Reference Robinson, Boon, Sawtell, James and Cross2008; Baumann and Hewitt, Reference Baumann and Hewitt2023) have said that radicle emergence was the criterion for germination. However, the photographs of Melaleuca alternifolia seeds in various stages of germination show the first stage as having a hypocotyl that is twice as long of the radicle (Pinheiro et al., Reference Pinheiro, de Medeiros, Hilst, Pinheiro and dos Dias2020), causing us to wonder if germination morphology in seeds with a spatulate embryo is like that in the other kinds of Myrtaceae seeds, i.e. the radicle does not grow until the hypocotyl has emerged from the seed.

A literature search was conducted to increase the size of our embryo database for the Myrtaceae. In total, we have information on embryo morphology for 240 species in 123 genera and 20 tribes of Myrtaceae (Supplementary Table S1). Some tribes of Myrtaceae have only one kind of embryo, e.g. Chamelaucieae has only linear-full and Heterophyxideae, Lindsaomyrteae, Lophostemoneae, Psiloxyleae, Syncarpieae and Syzygieae have only investing embryos (Table 1). Xanthomyrteae and Xanthostemoneae have only bent embryos; Tristaniopsideae only folded embryos; and Cloezieae, Leptospermeae, Melaleuceae, Metrosidereae, Osbornieae and Tristanieae only spatulate embryos. Backhousieae (bent, linear-full), Eucalypteae (folded, investing) and Kanieae (linear-full, spatulate) have two kinds of embryos, while the Myrteae have four kinds: bent, folded, investing and linear-full.

Table 1. Number of genera with different kinds of embryos in each tribe of Myrtaceae and occurrence of nondormancy (ND) and physiological dormancy (PD) in each tribe

Note: +, yes; −, no information.

According to Martin (Reference Martin1946), bent, folded, investing, linear and spatulate embryos have a central (axile) position inside the seed. Martin's family tree of seed phylogeny shows the linear embryo as being in about the middle of the tree, and the upward progression of embryos on the tree is linear → spatulate → bent → folded → investing. That is, the investing embryo is at the top of Martin's tree. However, when compared to the crown age of the various tribes of Myrtaceae (Thornhill et al., Reference Thornhill, Ho, Külheim and Crips2015), no clear pattern of phylogenetic relationships between the various kinds of embryos in Myrtaceae is evident. For example, the crown age of Lophostemoneae and Syzygieae with an investing embryo is 41.3 and 29.3 Ma, respectively, while that of Melaleuceae and Metrosidereae with spatulate embryos is 55.5 and 24.9 Ma, respectively. The crown age of Myrteae with bent, folded, investing and linear-full embryos is 50.7. The crown age of Xanthostemoneae and Backhousieae with a bent embryo is 55.6 and that of Backhousieae with bent and linear-full embryos is 18.5 Ma.

Vochysiaceae is the closest relative of Myrtaceae (Gonçalves et al., Reference Gonçalves, Shimizu, Ortiz, Jansen and Simpson2020), and living species of Vochysiaceae have seeds with folded, investing or spatulate embryos (Niembro, Reference Niembro1983; Garwood, Reference Garwood1998; Ferreira et al., Reference Ferreira, Davide and Tonetti2001; Kirkbride et al., Reference Kirkbride, Gunn and Dallwitz2006). Thus, it is not surprising to find these three kinds of embryos in various positions on molecular phylogeny trees of Myrtaceae based on either combined plastid or combined nuclear data (Wilson et al., Reference Wilson, Heslewood and Tarran2022). The presence of two or more kinds of embryos in four tribes of Myrtaceae (Table 1) suggests that there are some possible evolutionary relationships between kinds of embryos in this family that merit research, e.g. what is the origin of the bent and linear-full embryos in the Myrtaceae? Bent and linear-full embryos occur in Backhousieae and linear-full and spatulate embryos in Kanieae; however, the Myrteae have linear-full, bent, folded and investing embryos but no spatulate embryos.

Occurrence of seed dormancy: tribes, life forms and vegetation regions

Since the five kinds of embryos in seeds of Myrtaceae are fully developed (Fig. 1) and seeds are water permeable (e.g. Pérez-Fernández et al., Reference Pérez-Fernández, Lamont, Marwick and Lamont2000; Auld and Ooi, Reference Auld and Ooi2009; Hue et al., Reference Hue, Abdullah, Sinniah and Abdullah2013), freshly matured seeds are either ND or have PD. If seeds tested over a range of temperatures and in light and in dark germinate in less than about 4 weeks and show no increase in germination percentages when given a dormancy-breaking treatment, they are ND. On the other hand, if fresh seeds either do not germinate in about 4 weeks or exhibit a widening of range of environmental conditions (e.g. temperature) over which they germinated after receiving a dormancy-breaking treatment, they have PD (Baskin and Baskin, Reference Baskin and Baskin2014).

To enhance our database for seed dormancy/germination of Myrtaceae in Baskin and Baskin (Reference Baskin and Baskin2014), a literature search was conducted using the name of each tribe of Myrtaceae, seeds, semillas, sementes, germination, germinação and germinación. In total, information on seed dormancy/germination was found for 571 species of Myrtaceae (Supplementary Table S2). Some species in all 20 tribes of Myrtaceae have ND seeds, and species in 8 tribes have seeds with PD (Table 1). For many tribes, however, the absence of PD in the tribe may be due to a lack of detailed germination studies for members of that tribe.

Each of the 571 species was recorded by life form (tree or shrub) in the vegetation region in which it grew (Supplementary Table S2). Then, the proportion of tree and shrub species in each vegetation region with ND seeds or with PD was calculated to create a seed dormancy profile for the Myrtaceae (Table 2). Overall, seeds of 55.6% of the Myrtaceae species had ND seeds, and the other 44.4% had seeds with PD. The highest number of tree species was recorded for tropical rainforest and semi-evergreen rainforest, and that for shrubs was the matorral (sclerophyllous woodlands with winter rain). The relative importance of ND and PD trees and shrubs varied with the vegetation region. In rainforests, the percentage of trees and shrubs with either ND or PD was almost equal (c. 50%). In semi-evergreen rainforests and savannas, both trees and shrubs had a higher percentage of ND than PD. In the matorral and broad-leaved evergreen forests, trees had a higher percentage of ND than shrubs, while shrubs had a higher percentage of PD than trees. In hot deserts (trees) and grasslands (shrubs), all species had ND seeds. Tropical montane trees had a higher percentage of PD (68.4) than ND (31.6), but 50% of shrubs had ND seeds and 50% seeds with PD. In dry deciduous forests, trees had 42.9 and 57.1% ND and PD, respectively, but all shrubs had seeds with PD.

Table 2. Seed dormancy profile for trees and shrubs of Myrtaceae in different vegetation regions

Not only did the rainforest and semi-evergreen rainforest have the highest number of species of trees (93 and 104, respectively), but they also had 12 and 9 tribes of Myrtaceae, respectively (Table 3). Shrubs in the rainforest and semi-evergreen rainforest were represented by 3 and 12 tribes of Myrtaceae, respectively. In the other seven vegetation regions, both trees and shrubs were represented by 0–5 tribes. Trees were represented by 0 and 5 tribes in grassland and savanna, respectively, and shrubs by 0 and 5 tribes in hot desert and broad-leaved evergreen forest, respectively.

Table 3. Tribes of Myrtaceae, vegetation regions (1–9)a and life form (tree or shrub)

a Vegetation regions: 1, rainforest; 2, semi-evergreen rainforest; 3, tropical montane; 4, tropical dry deciduous; 5, savanna; 6, hot desert; 7, matorral; 8, broad-leaved evergreen and 9, temperate grassland.

Dormancy-break in seeds of Myrtaceae

Since Myrtaceae is mostly a tropical family, it comes as no surprise that the breaking of PD in seeds of many members of this family occurs at warm conditions suitable for germination. Thus, in many studies, seeds have been sown in nurseries or greenhouses without receiving any dormancy-breaking treatments (Supplementary Table S2), and the number of days until seeds germinated was monitored. Methods used in laboratories to break seed dormancy and promote germination include treatment with GA3 (Cochrane et al., Reference Cochrane, Kelly, Brown and Cunneen2002; Scalon et al., Reference Scalon, Filho and Rigoni2004; Liang et al., Reference Liang, Liu, Huang, Wei, Ye, Luo and Xiong2013; Saldías and Velozo, Reference Saldías and Velozo2014; Damiani et al., Reference Damiani, da Silva, Goelzer and Déo2016; Griebeler et al., Reference Griebeler, Araujo, Rorato, Turchetto, Tabaldi, Barbosa and Berghetti2019; Mali et al., Reference Mali, Jain, Yadav, Sharma and Singh2021; Santos et al., Reference Santos, Santos, Pinto, Dresch, Scalon and Torales2022), potassium nitrate (Liang et al., Reference Liang, Liu, Huang, Wei, Ye, Luo and Xiong2013), smoke-infused water (Cochrane et al., Reference Cochrane, Kelly, Brown and Cunneen2001), sodium nitrite and potassium cyanide (Bardales et al., Reference Bardales, Pisco, Flores, Mashacuri, Ruíz, Correa and Gómez2014). Germination also has been promoted by mechanical scarification (Gentil and Ferreira, Reference Gentil and Ferreira1999; Martinotto et al., Reference Martinotto, Paiva, Santos, Soares, Nogueira and Silva2007; Tafarel et al., Reference Tafarel, Silvestre, Pansera, Rodrigues and Sartori2021) and by removing the seed coat from the embryo (Rizzini, Reference Rizzini1970; Gentil and Ferreira, Reference Gentil and Ferreira1999). In a study of the cold hardiness of 15 species of Eucalyptus being considered for possible introduction into Ireland, 4 weeks of cold stratification increased germination (compared to fresh seeds) for only one species (Afroze et al., Reference Afroze, Douglas and Grogan2021). The positive response of seeds to treatments such as GA3 and scarification indicates that seeds have nondeep PD.

Seed germination of Myrtus communis is promoted by soaking seeds in water, treatment with GA3 and cold stratification (Benvenuti and Macchia, Reference Benvenuti and Macchia2001). Ballesteros et al. (Reference Ballesteros, Meloni and Bacchetta2015) recommended 3 months of cold stratification to break dormancy of M. communis seeds. After cold stratification, Benvenuti and Macchia (Reference Benvenuti and Macchia2001) obtained higher germination percentages at 25–30°C than at 10–20°C. We conclude that seeds of this species also have nondeep PD.

If GA3 and scarification do not promote germination and if seeds require a long period of time (40–150 d) to germinate (Rizzini, Reference Rizzini1970; Smith-Ramírez et al., Reference Smith-Ramírez, Armesto and Figueroa1998; Santos et al., Reference Santos, Ferreira and Aquilla2004; Scalon et al., Reference Scalon, Filho and Rigoni2004; Masetto et al., Reference Masetto, Davide, Faria, da Silva and Rezende2009; Simpson, Reference Simpson2011; Saldías and Velozo, Reference Saldías and Velozo2014), they may have intermediate or deep PD. Unfortunately, no studies have been done to determine if the long-germinating seeds of Myrtaceae have intermediate or deep PD.

There are six types of nondeep PD, and they can be distinguished by the changes in temperature requirement for germination during the dormancy-breaking treatment (Types 1, 2 and 3) or by the temperature range over which seeds will germinate when dormancy is broken (Types 4, 5 and 6) (Baskin and Baskin, Reference Baskin and Baskin2014; Soltani et al., Reference Soltani, Baskin and Baskin2017). In the early stages of dormancy-break, seeds with Types 1, 2 and 3 dormancy germinate at low, high and intermediate temperatures, respectively. As dormancy-break continues, seeds with Types 1 and 2 dormancy exhibit an increase in the maximum temperature for germination and a decrease in the minimum temperature for germination, respectively, while seeds with Type 3 dormancy exhibit an increase in the maximum and a decrease in the minimum temperatures for germination. In the early stages of dormancy-break, seeds with Type 6 dormancy germinate over a range of low to high temperatures. During the continuation of dormancy-break, seeds with Type 6 dormancy do not exhibit an increase in the range of temperatures over which they can germinate, but germination percentages may increase. Seeds with Types 4 and 5 dormancy gain the ability to germinate only at high and low temperatures, respectively.

Seeds of Myrtaceae with PD have been tested at 20, 25 and 30°C (Hossel et al., Reference Hossel, Hossel, Júnior, Mazzaro and Fabiane2017; Paim et al., Reference Paim, Avrella, Emer, Caumo, Alver and Fior2018; Souza et al., Reference Souza, Souza and Panobianco2018; Leão-Araújo et al., Reference Leão-Araújo, Souza, Peixoto and Gomes-Júnior2019); 25, 30 and 30/20°C (Mugnol et al., Reference Mugnol, Quintáo, da Silva, Elisa and Mara2014) and 20, 25, 30, 35 and 30/20°C (Maeda et al., Reference Maeda, Bovi, Bovi and do Lago1991; Masetto et al., Reference Masetto, Davide, Faria, da Silva and Rezende2009). Among these studies, the ability of seeds to germinate at 20°C varied between the species. Seeds of Psidium cattleianum germinated to low percentages at 20°C (Hossel et al., Reference Hossel, Hossel, Júnior, Mazzaro and Fabiane2017), while those of Campomanesia adamantium (Leão-Araújo et al., Reference Leão-Araújo, Souza, Peixoto and Gomes-Júnior2019), C. guazumifolia (Souza et al., Reference Souza, Souza and Panobianco2018) Eugenia pleurantha (Masetto et al., Reference Masetto, Davide, Faria, da Silva and Rezende2009), Myrceugenia myrtoides (Paim et al., Reference Paim, Avrella, Emer, Caumo, Alver and Fior2018) and Syzygium aromaticum (Maeda et al., Reference Maeda, Bovi, Bovi and do Lago1991) germinated to high percentages. Seeds of P. guineense germinated at 25, 30 and 30/20°C, and after both 20 and 42 d of incubation, the highest percentage was at 30/20°C. After 42 d of incubation, the germination percentage had increased at 30°C (Mugnol et al., Reference Mugnol, Quintáo, da Silva, Elisa and Mara2014).

Some studies have tested seeds with PD at 5, 10 and 15°C. No seeds of Rhodomyrtus tomentosa germinated at 5 or 10°C (Liang et al., Reference Liang, Liu, Huang, Wei, Ye, Luo and Xiong2013) or at 10 or 15°C (Hue et al., Reference Hue, Abdullah, Sinniah and Abdullah2013). There was little or no germination of seeds of Acca sellowiana, Campomanesia xanthocarpa, Eugenia involucrata or E. pyriformis at 15°C (Gomes et al., Reference Gomes, Oliveira, Ferreira and Batista2016), but seeds of Psidium guineense germinated to 35% at this temperature (Santos et al., Reference Santos, Queiróz, Bispo and Dantas2015). Seeds of Darwinia species and Melaleuca species (with PD when freshly matured) germinated at 15°C (Cochrane et al., Reference Cochrane, Kelly, Brown and Cunneen2002), but the full range of temperatures for germination of these seeds was not determined.

The general conclusion from studies in which seeds of Myrtaceae were tested over a range of temperatures is that the highest germination percentages were at high temperatures. These results suggest that seeds have Type 4 nondeep PD. However, due to a lack of detailed studies on the temperature requirements for germination during the period of dormancy-break, we cannot rule out the possibility that some species have Type 6 nondeep PD (or other types of nondeep PD) with a temperature range of 20 to about 35°C for germination after PD is broken. Much more research needs to be done on the temperature requirements for germination during the dormancy-breaking period of seeds of Myrtaceae.

In Supplementary Table S2, we have recorded the temperatures (or conditions such as nursery or greenhouse) at(in) which a high percentage of the seeds of each species germinated. For 320 species listed in tropical vegetation regions, only 5 species (1.6%) have 15°C (often along with temperatures >15°C) listed as suitable for high germination; 3 of the species are in the Myrteae and one each in the Eucalypteae and Melaleuceae. For 251 species listed for temperate vegetation regions, 59 species (23.5%) have 15°C listed as a temperature for high germination. All 59 species occur in the matorral, and they belong to the Chamelaucieae, Eucalypteae or Melaleuceae, which are dry-fruited tribes. The ability of seeds of Myrtaceae to germinate at relatively low temperatures, e.g. 15°C, especially in the matorral indicates that germination can be delayed until the onset of the cool, wet season in winter. That is, dormancy-break occurs in summer and seeds germinate when the cool, wet season begins; however, no studies have been done that inform us as to what type of nondeep PD these seeds have.

Seed germination requirements

Many seed germination studies of Myrtaceae species have been conducted in nurseries, shade houses and greenhouses at near natural temperature regimes (Supplementary Table S2). The temperature at which a high germination percentage was obtained is available for 246 species (Supplementary Table S2), and the mean (±SE) of these temperatures is 22.5 ± 0.2°C. Determinations of the light (L)–dark (D) requirements for seed germination have been made for 34 species (Supplementary Table S2): 15 species, L > D; 14, L = D; 3, D > L; and 2 species with mixed results, i.e. one paper reported L = D and another D > L. Germination of Eucalyptus marginata seeds was significantly lower in white light than in darkness or in light with peak wavelengths of 430, 450, 490, 520, 570, 640 and 720 nm, as transmitted through Kodak Wratten photographic coloured filters (Rokich and Bell, Reference Rokich and Bell1995). Germination of E. calophylla seeds was significantly reduced in white light and at wavelengths of 570 and 640 nm.

Seeds of Myrtaceae differ in their ability to germinate during and after water stress, and not surprisingly the ND, desiccation-sensitive seeds of Campomanesia pubescens (Dousseau et al., Reference Dousseau, Alvarenga, Guimarães, lara, Custódio and Chaves2011) and Eugenia pyriformis (Andrade and Ferreira, Reference Andrade and Ferreira2000) are dispersed at the onset of the rainy season in the seasonally dry Cerrado of Brazil (Escobar et al., Reference Escobar, Rubio de Casas and Morellato2021). The ND seeds of Myrcia guianensis and M. splendens, which also grow in the Cerrado of Brazil, are dispersed at the onset of the rainy season and mid-rainy season, respectively. Thus, seed dispersal in these four species occurs at a time when soil moisture would be adequate for seed germination.

Seeds of Eugenia brasiliensis, E. involucrata, E. pyriformis and E. uniflora germinated to 100, 84, 66 and 91% at 0.0 MPa, respectively, but germination of each species decreased with water stress, e.g. 44, 8, 0 and 39% at −1.5 MPa, respectively; and 0, 2, 0 and 0%, respectively, at −2.0 MPa (Inocente and Barbedo, Reference Inocente and Barbedo2019). Seeds of E. umbelliflora were dispersed during the dry season in restinga vegetation in Brazil (Braz and de Mattos, Reference Braz and Mattos2010). At 0 and −0.37 MPa, seeds of E. umbelliflora germinated to 88 and 38%, respectively, and 52 and 54 d, respectively, were required for seeds to reach 50% of final germination. Further, moisture content (MC) of fresh seeds was 45–50%, and after drying at 68% relative humidity for c. 17 d, it was 28%, at which point only 30% of them germinated. At −0.1, −0.4 and −0.7 MPa, seeds of Melaleuca nematophylla germinated to 58.4, 36.3 and 0.5%, respectively (Merino-Martín et al., Reference Merino-Martín, Courtauld, Commander, Turner, Lewandrowski and Stevens2017). Seeds of Eucalyptus caesia subsp. caesia, E. ornata, and E. salubris germinated to 95–100% at −0.1 MPa; to 95, 95 and 70%, respectively, at −0.4 MPa and to 70, 35 and 8%, respectively, at −0.7 MPa (Rajapakshe et al., Reference Rajapakshe, Turner, Cross and Tomlinson2020). However, seeds of E. salmonophloia germinated to 50, 4 and 0% at −0.1, −0.4 and −0.7 MPa, respectively. Thus, seeds of the range-restricted E. caesia subsp. caesia and E. ornata were more tolerant of water stress during germination than those of the widely distributed E. salmonophloia.

Seeds of Eucalyptus macrocarpa and E. tetragona from deep sand habitats and those of E. loxophleba and E. wandoo from lateritic loam habitats germinated to c. 100% at a soil moisture potential of −0.1 MPa (Schütz et al., Reference Schütz, Milberg and Lamont2002). At −0.5 MPa, seeds of E. tetragona germinated to c. 95% and those of the other three species to 70–75%. At −1.0 MPa, however, the only germination (c. 5%) was for seeds of E. tetragona. Seeds of E. todtiana incubated on a moist substrate for 24 h at 15°C reached an MC of c. 50%. However, when seeds at 50% MC were placed on dry filter paper in an ‘air-blown cabinet’ at 23° and 55% relative humidity for 48 h MC decreased to c. 10% (Pérez-Fernández et al., Reference Pérez-Fernández, Lamont, Marwick and Lamont2000). Seeds dried for 48 h germinated to 100% and reached 50% germination in c. 9 d. Thus, seeds of E. todtiana recovered from dehydration and germinated.

Seeds of Eucalyptus brassiana, E. camaldulensis, E. grandis, E. saligna, E. tereticornis and E. urophylla germinated to 8, 39, 9, 4, 46 and 45%, respectively, at a water stress of −0.6 MPa but to only 0, 5, 0, 0, 5 and 9%, respectively, at −0.8 MPa (de Sá-Martins et al., Reference de Sá-Martins, Cleiton-José, Rocha-Faria and de Melo2019). In a NaCl solution with an osmotic potential of −1.5 MPa, seeds of E. brassiana, E. camaldulensis, E. grandis, E. saligna, E. tereticornis and E. urophylla germinated to 9, 18, 4, 4, 18 and 6%, respectively.

Some species of Myrtaceae grow in habitats that are submerged in water for part, or all, of the year. Seeds of Leptospermum lanigerum and Melaleuca squarrosa germinated under water, but flooding reduced seedling growth and survival (Zacks et al., Reference Zacks, Greet, Walsh and Raulings2018). The recalcitrant seeds of Eugenia stipitata submerged in 6 cm of water began to germinate after 2 months and after 1 year 87% had germinated (Calvi et al., Reference Calvi, Anjos, Kranner, Pritchard and Ferraz2017). Most seeds of Melaleuca ericifolia did not germinate while flooded, but even after 3–4 weeks of flooding, seeds germinated to high percentages when transferred to moist germination pads in Petri dishes (Ladiges et al., Reference Ladiges, Foord and Willis1981). Seedlings from the few seeds that germinated under water did not grow past the cotyledon stage while flooded. Fleshy fruits of Blepharocalyx cruckshanksii and Luma apiculata growing in forested wetlands of south-central Chile floated for 37 and 53 d, respectively (Mora and Smith-Ramírez, Reference Mora and Smith-Ramírez2017). After 90 d in water, seeds of both species germinated (c. 80%) inside the fruits, when fruits were removed from water and placed in moist soil. The authors concluded that the fleshy fruits promoted dispersal, but after fruits became lodged on moist soil as water receded seeds inside them could germinate readily.

There is concern that global warming will modify the environment to the extent that dormancy-break, germination and seedling survival will be negatively impacted. In a study of 100 plant species growing in Western Australia that included 37 Myrtaceae species/taxa, Eucalyptus kruseana, E. nigrifunda, E. pimpiniana, E. jimberlanica and Rhodanthe pyrethrum germinated to higher percentages when incubated at temperatures lower than those in the field during the wet season (Cochrane, Reference Cochrane2020). One species germinated to the highest percentages at field temperature during the wet season, while 31 species germinated to higher percentages at temperatures higher than those in the field during the wet season. Thus, based on this small sample of Myrtaceae species, it appears that increased temperatures due to global warming may not significantly impede the regeneration of species of Myrtaceae from seeds. For 26 species of Eucalyptus in Western Australia, modelling of seed germination response to temperature revealed that the majority of species will be able to germinate in the future, especially in the cool winter months (Cochrane, Reference Cochrane2017).

Although temperatures may be favourable for seed germination of many Myrtaceae species in the future, the question is will there be adequate precipitation for seedling survival? In other words, if precipitation decreases in the driest months will there be enough soil moisture to sustain the seedlings? Some modelling has been done to look at future precipitation patterns, but more is needed. Barrientos-Díaz et al. (Reference Barrientos-Díaz, Báez-Lizarazo, Enderle, Segatto, Reginato and Turchetto-Zolet2024) predicted that future temperature and rainfall conditions will be favourable for species of Myrteae to live in the Atlantic Forest of Brazil. However, predictions for the future distribution of Eugenia uniflora in South America suggest that Argentina and Paraguay will not have suitable habitat for this species, but populations of it may increase on the Brazilian Plateau (Turchetto-Zolet et al., Reference Turchetto-Zolet, Salgueiro, Turchetto, Cruz, Veto, Garros, Segatto, Freitas and Margis2016).

Tribes and species of Myrtaceae with desiccation-sensitive seeds

Information was found for desiccation sensitivity of 58 species of Myrtaceae, and all of them belonged either to the Myrteae (33 species) or Syzygieae (25 species) (Table 4). According to Wilson (Reference Wilson and Kubitzki2010), all the genera of Myrteae and Syzygieae represented in Table 4 have fleshy fruits. Seven species of Myrteae have intermediate seed storage behaviour, and the other 26 have recalcitrant seeds. The species of Myrteae with intermediate storage behaviour have seeds with linear-full embryos, and those that are desiccation-sensitive have seeds with investing, folded or linear-full embryos. The 25 species of Syzygieae have desiccation-sensitive seeds, and all have investing embryos.

Table 4. Species of Myrtaceae with desiccation-sensitive (recalcitrant [R] or intermediate [I]) seed storage behaviour

Among five Brazilian species of Eugenia with desiccation-sensitive seeds, the speed of seed drying and the speed of germination help explain differences in geographical range (Rodrigues et al., Reference Rodrigues, Silva, Ribeiro, Loaiza-Loaiza, Alcantara, Komatsu, Barbedo and Steiner2022). For seeds of E. uniflora, E. involucrata, E. pyriformis, E. brasiliensis and E. astringens, the water content threshold that decreased germination to c. 50% was 0.44, 0.33, 0.33, 0.25 and 0.25 g H2O (g DW)−1, respectively, and the species occurred in four, three, two, one and one morphoclimatic domain(s) (based on temperature and precipitation data) in Brazil, respectively. However, under laboratory conditions, seeds of E. uniflora had the second highest rate (speed) of germination and the slowest rate of water loss compared with the other species. The authors concluded that rapid germination and slow seed drying help explain why E. uniflora has a wider geographical distribution than the other four species.

Plantlet production from seed fragments (totipotency)

One consequence of seed predation is that the predator may not consume the whole seed, especially in the case of large seeds (Vallejo-Marín et al., Reference Vallejo-Marín, Domínguez and Dirzo2006; Pérez et al., Reference Pérez, Shiels, Zaleski and Drake2008; Loayza et al., Reference Loayza, Gachon, García-Guzmán and Carvajal2015). In some species, if fragments of seeds have an intact embryonic axis, there is a possibility that a plantlet will be produced. For example, the large recalcitrant seeds of Myrcianthes coquimbensis, a threatened Myrtaceous shrub in the Atacama Desert of Chile, will produce a plantlet if up to 75% of seed mass is removed from either mature or immature seeds (Loayza et al., Reference Loayza, Gachon, García-Guzmán and Carvajal2015).

Normal plantlet development occurred when seeds of Eugenia stipitata subsp. sororia (Anjos and Ferraz, Reference Anjos and Ferraz1999; Calvi et al., Reference Calvi, Anjos, Kranner, Pritchard and Ferraz2017), E. brasiliensis, E. involucrata and E. uniflora (Silva et al., Reference Silva, Bilia and Barbedo2005) were cut into two parts. Seeds of E. pyriformis cut in half longitudinally or transversally and those cut transversally into two parts, i.e. one-fourth of the seed and three-fourths of the seed, produced normal plantlets (Silva et al., Reference Silva, Bilia, Maluf and Barbedo2003). Normal plantlet development occurred for seeds of E. cerasiflora, E. pruinosa and E. umbelliflora cut in half transversally or longitudinally and from three-fourths of a seed (Delgado et al., Reference Delgado, Melo and Barbedo2010). When seeds were cut into four equal parts (in a linear fashion), normal plantlets developed from one-fourth (external/end part) of a seed for E. cerasiflora and E. pruinosa but not for E. umbelliflora. Also, normal plantlet development occurred from one-fourth of a seed (internal/central part) for E. cerasiflora and E. umbelliflora but not for E. pruinosa.

In some species, the percentage of plantlet development/germination was higher for pieces of seeds than for intact seeds, e.g. E. cerasiflora and E. pruinosa (Delgado et al., Reference Delgado, Melo and Barbedo2010), but often the percentage for seed fragments and intact seeds did not differ significantly, e.g. E. umbelliflora (Delgado et al., Reference Delgado, Melo and Barbedo2010) and E. uniflora (Silva et al., Reference Silva, Bilia and Barbedo2005). However, plantlet formation from E. pyriformis seeds cut into 0, 2 and 4 pieces was 97, 73 and 62%, respectively (Costa et al., Reference Costa, Pinto, Morais, Oliveira and Barreto2017). The production of normal plantlets from seeds of E. uniflora cut into two parts was higher for seeds produced from cross- than from self-pollinated flowers (Fidalgo et al., Reference Fidalgo, Cécel, Mazzi and Barbedo2019).

The regeneration of roots and plantlets from fragments of Eugenia seeds occurs in seeds taken from both immature and mature fruits (Teixeira and Barbedo, Reference Teixeira and Barbedo2012; Amador and Barbedo, Reference Amador and Barbedo2015; Delgado and Barbedo, Reference Delgado and Barbedo2020). However, there is a reduction in the success of plantlet formation from E. pyriformis seed fragments with an overall decrease in seed size, which is related to a number of seeds in fruit (Prataviera et al., Reference Prataviera, Lamarca, Teixeira and Barbedo2015). Although seed fragments of E. pyriformis (Amador and Barbedo, Reference Amador and Barbedo2011), E. brasiliensis, E. uniflora (Amador and Barbedo, Reference Amador and Barbedo2015) and E. stipitata (Calvi et al., Reference Calvi, Anjos, Kranner, Pritchard and Ferraz2017) can form a plantlet, only one plantlet is produced if the incision does not completely separate the seed parts. That is, if there is a connection between two seed parts only one of them produces roots and a plantlet.

Normal plantlet development occurred when seeds of Syzygium myrtifolium were cut into two parts longitudinally, but when seeds were cut transversally into two parts only one part produced a plantlet (Tsan, Reference Tsan2023). When a seed was cut into four parts longitudinally, at least one of the parts produced a plantlet, with the central and right fractions being the most likely to do so. However, when cut into two longitudinal and two transverse (i.e. four) parts, only the top left and top right parts produced a plantlet.

Effects of fire (heat and smoke) on seed germination

The appearance of Myrtaceae seedlings in the field after a fire (e.g. Mount, Reference Mount1969; Williams, Reference Williams2000; Wright, Reference Wright2018; Wright et al., Reference Wright, Albrecht, Silcock, Hunter and Fensham2019) has prompted people to conduct experiments on the effects of heat and smoke on seed germination. Heat treatments on seeds of various species have revealed that temperatures simulating those in/at the soil surface during a fire can increase, decrease or have no effect on germination percentages (Table 5). Smoke, in general, either increases or decreases germination percentages of Myrtaceae seeds (Table 6). Seeds of Baeckea utilis did not respond to heat in the absence of smoke, but they responded to smoke in the absence of heat (Thomas et al., Reference Thomas, Morris and Auld2007). For seeds of Kunzea ambigua and K. capitata, there was an interaction between incubation temperature (15 and 25°C), water stress (0 and −0.9 MPa) and fire cues (heat and smoke) (Thomas et al., Reference Thomas, Morris, Auld and Haigh2010). Fire cues increased germination percentages at 15 and 25°C across the range of water stress, i.e. fire cues increased seed tolerance to water stress.

Table 5. Effect of dry heat treatments on seed germination of species of Myrtaceae

All studies were conducted in Australia unless otherwise noted.

a Study conducted in New Zealand.

b Increase in number of seedlings in soil seed bank samples after soil heating.

Table 6. Effect of smoke and/or smoke extracts on seed germination of species of Myrtaceae

a Seeds tested at 26/30 and 33/18°C, respectively.

Another aspect of fire in a plant community is that the smoke contains various compounds, including cyanohydrin (glyceronitrile, which in the presence of water releases cyanide), ethylene, karrikins (especially karrikin-1), nitrate and nitric oxide, that are known to promote seed germination (Flematti et al., Reference Flematti, Merritt, Piggott, Trengove, Smith, Dixon and Ghisalberti2011, Reference Flematti, Waters, Scaffidi, Merritt, Ghisalberti, Dixon and Smith2013; Soós et al., Reference Soós, Badics, Incze and Balázs2019; Cao et al., Reference Cao, Schöttner, Halitschke, Li, Baldwin, Rocha and Baldwin2021, Reference Cao, Baskin, Baskin and Li2023; Kępczyański and Kępczyańska, Reference Kępczyński and Kępczyńska2023). However, only karrikins and cyanohydrins can persist in the upper layers of the soil after a fire (Flematti et al., Reference Flematti, Waters, Scaffidi, Merritt, Ghisalberti, Dixon and Smith2013). Smoke also contains compounds that are structurally similar to karrikins, i.e. contain a butanolide ring that inhibits germination (Light et al., Reference Light, Burger, Staerk, Kohout and Van Staden2010; Burger et al., Reference Burger, Pošta, Light, Kulkarni, Viviers and Van Staden2018). Soós et al. (Reference Soós, Badics, Incze and Balázs2019) suggested that after a fire both germination inhibitors and promotors are in the surface layers of soil. However, the promotors cannot be effective in stimulating germination until rain water has removed the inhibitors.

If a fire occurs while seedlings/juveniles are relatively small, they may not be robust/resilient enough to tolerate fire and are killed (e.g. Fordyce et al., Reference Fordyce, Eamus, Duff and Williams1997; Tozer and Bradstock, Reference Tozer and Bradstock1997; Wardell-Johnson, Reference Wardell-Johnson2000; Fujita, Reference Fujita2021; Plumanns-Pouton et al., Reference Plumanns-Pouton, Swan, Penman, Collins and Kelly2023). Thus, regeneration from seeds is not successful if the fire interval is more frequent than the time required for young plants to reach a fire-tolerant size.

Various species of Myrtaceae produce new stems from buds if the aerial portion of the plant is damaged/destroyed, as for example by fire. Epicormic buds (dormant buds located under the bark), arise from meristematic cells (epicormic strands) that are inside the bark, often at the junction of the bark and vascular cambium, e.g. Eucalyptus and Melaleuca (Burrows, Reference Burrows2002; Clarke et al., Reference Clarke, Lawes, Midgley, Lamont, Ojeda, Burrows, Enright and Knox2013). Lignotubers which form at the base of the stem, e.g. in many species of Eucalyptus, have many buds that can grow if the stem is killed. The development of a lignotuber begins shortly after seedling emergence, and it increases in size as the plant grows (Fordyce et al., Reference Fordyce, Eamus and Duff2000; Nicolle, Reference Nicolle2006). Lignotubers were initiated on seedlings of Eucalyptus cinerea by the time plants were 6 weeks old (Graham et al., Reference Graham, Wallwork and Sedgley1998). After 9 months of growth, the size of the lignotubers on Eucalyptus obliqua juveniles derived from seeds from 13 provenances in Australia was inversely related to mean annual precipitation in the original habitat (Walters et al., Reference Walters, Bell and Read2005). Interestingly, a molecular marker for lignotuber formation (Elig) has been identified in Eucalyptus (Bortoloto et al., Reference Bortoloto, Fuchs-Ferraz, Kettener, Rubia, González, de Souza, Oda, Rossini and Marino2020).

Buds that can replace damaged aerial stems also occur on rhizomes. For example, Eugenia dysenterica and E. pumicifolia, which grow in the fire-prone Cerrado of Brazil, have a woody rhizome covered with periderm. Silva et al. (Reference Silva, Ferraro, Ogando, Aguiar and Appezzato-Da-Gloria2020) found numerous buds (254–517 per plant) on the upper surface of the rhizome of each species.

Global warming is having significant effects on fire regimes, especially in fire-prone habitats (Ooi et al., Reference Ooi, Tangney, Auld, Baskin and Baskin2022). There are increases in the severity and frequency of fires, as well as changes in the time of year when fires occur (Ooi et al., Reference Ooi, Tangney, Auld, Baskin and Baskin2022). Even if species of Myrtaceae resprout after fire, increased fire intensity and frequency can cause shifts from wet- to dry-plant communities (Furland et al., Reference Furlaud, Prior, Williamson GJ and Bowman2021; Fensham et al., Reference Fensham, Laffineur and Browning2024). Further, the pathogenic fungus Austropuccinia psidii may retard the regrowth of new stems and leaves following a fire. The impact of A. psidii on regrowth of tissues on nine Myrtaceae species following fire in a coastal heathland in New South Wales (Australia) varied between species and ranged between minor leaf damage to die-back and eventual death of the tree (Pegg et al., Reference Pegg, Entwistle, Giblin and Carnegie2020).

For some species, e.g. Eucalyptus pauciflora in the subalpine zone in Victoria, Australia, increased fire frequency has raised serious concerns about the ability of the species to persist in its natural habitat (Coates, Reference Coates2015). Increased temperatures, decreased precipitation and increased fire frequency are expected to negatively impact the tropical montane species Melaleuca uxorum and could result in its extinction as well as the loss of the local specialized flora in the habitat of this species being replaced by widely distributed species (Ford and Hardesty, Reference Ford and Hardesty2012).

Formation of soil seed banks

In 170 soil seed bank studies, in which soil samples were collected after the seed germination season but before newly matured seeds were dispersed, i.e. samples potentially had at least a short-lived persistent soil seed bank, we found nine papers that contained information for species of Myrtaceae. Seven species in six tribes of Myrtaceae were listed in these nine papers (Table 7). The number of seeds per species in the seed bank ranged from 1 to 32 m−2. However, for Eucalyptus grandis, the number of seeds was not given (Gonçalves et al., Reference Gonçalves, Martins, Marins and Felfili2008), and, for Tristaniopsis sp., none of the seeds found in the soil samples germinated (Graham and Page, Reference Graham and Page2018). However, some soil seed bank studies conducted in habitats where species of Myrtaceae were growing did not contain any seeds of Myrtaceae (e.g. Vlahos and Bell, Reference Vlahos and Bell1986; Yates et al., Reference Yates, Taplin, Hobbs and Bell1995; Sem and Enright, Reference Sem and Enright1996; Wang, Reference Wang1997; Hamilton-Brown et al., Reference Hamilton-Brown, Boon, Raulings, Morris and Robinson2009; Bechara et al., Reference Bechara, Salvador, Ventura, Topanotti, Gerber, Cruz and Simonelli2020; Neto et al., Reference Neto, Martins and Silva2021; Kraaij et al., Reference Kraaij, Geerts and Malan2024).

Table 7. Soil seed bank of Myrtaceae

To help determine how long seeds of Myrtaceae live in the soil, seeds of various species have been placed in mesh bags and buried in the field. At intervals over a 1- to 3-year period, some of the buried seeds were exhumed, and the number of viable seeds was determined (Table 8). In general, seeds do not live for long periods of time in the soil. Of the 11 species listed in Table 8, only Kunzea ambigua and K. capitata had >50% viable seeds after 2 years (Auld et al., Reference Auld, Keith and Bradstock2000).

Table 8. Longevity of seeds of Myrtaceae placed in mesh bags and buried in soil in the field

a All buried seeds had germinated after 1 month; thus, no nongerminated viable seeds were present at the end of the study.

b No information.

Yates et al. (Reference Yates, Taplin, Hobbs and Bell1995) buried seeds of Eucalyptus salmonophloia in soil at a depth of 1 cm in 3-cm-diameter areas in Western Australia in summer, autumn, winter and spring. Then, 2, 6 and 12 months after burial in each season, soil cores (from inside the 3-cm-diameter areas) were removed and germination of seeds was monitored. Some seeds buried in summer survived and germinated after 12 months of burial, but few or no seeds buried in autumn, winter or spring survived and germinated after 12 months of burial.

Seeds of 10 species of Myrtaceae were sown in moist soil in a shade house in Western Australia, and seed viability was determined initially and after 1 year: Agonis linearifolia, 80 (initially) and 5% (after 1 year) viable seeds; Astartea fascicularis, 47 and 14%; Baeckea camphorosmae, 52 and 30%; Calytrix breviseta var. breviseta, 63 and 18%; C. depressa, 54 and 20%; Verticordia aurea, 60 and 40%; V. chrysantha, 63 and 38%; V. densiflora, 58 and 23%; V. eriocephala, 20 and 11% and V. huegelii, 26 and 3% (Roche et al., Reference Roche, Dixon and Pate1997a).

Seeds of Baeckea gunniana and B. utilis were buried in the Ginini Flats subalpine bog complex of the Brindabella Mountains (Australian Alps) in southeastern Australia (Guja and Brindley, Reference Guja and Brindley2017). After 27 months of burial, the exhumed seeds of both species germinated to c. 97%. The germination of B. utilis seeds at 25/15 and 20/10°C exhumed after 3, 6, 9, 12, 21 and 27 months revealed that dormancy cycling was occurring with seeds exhumed after 3, 12 and 27 months having the highest germination percentages and those exhumed after 9 and 21 months the lowest percentages.

The application of smoke to field sites has been shown to promote the germination of seeds in the soil. For example, smoke fumigation in Banksia woodland in Western Australia significantly increased seed germination of 15 plant taxa, but none of them were Myrtaceae (Dixon et al., Reference Dixon, Roche and Pate1995). Aerosol smoke and smoke-infused water applied to soil seed bank samples collected in Western Australia promoted seed germination of native grasses, sedges, herbs and woody species, including a few seeds of Eucalyptus sp., as well as seeds of weedy herbs in families other than Myrtaceae (Cochrane et al., Reference Cochrane, Monks and Lally2007). In Queensland (Australia), soil seed bank samples from nonburned forest/woodland/shrubland habitats at four sites were subjected to heat and/or smoke treatments (Page, Reference Page2009). Following a fire in the four sites, additional soil samples were collected and germination of seeds in them was compared with that of seeds in the treated, nonburned samples. The number of seedlings (m−2) in the heat and smoke-treated samples was higher than that in the control samples with no treatments. However, the number of species and the number of seedlings that emerged from the four sites after the fire were higher than in the nonburned control, except in the burned mixed Eucalyptus forest with lower numbers than in the control.

Smoke treatments have been applied in the field in relation to using the soil seed bank from Eucalyptus/Banksia woodlands in Western Australia as a source of seeds for rehabilitation of surface-mined sites (Roche et al., Reference Roche, Koch and Dixon1997b). Following smoke treatments of soil in the field, the number of species and the number of seedlings increased significantly, but often the density of Myrtaceae seedlings was low. For example, the density of Eucalyptus marginata seedlings increased from 0 to 1.67 m−2 after smoke treatments of soil in Western Australia (Roche et al., Reference Roche, Koch and Dixon1997b). Soil samples collected in a plant community dominated by Eucalyptus cneorifolia in South Australia were subjected to heat (80° for 60 min), smoke (from burning barley hay) and heat + smoke treatments in a greenhouse. Compared with the control, all treatments increased the germination of Thryptomene ericaea; and heat + smoke increased the germination of Baeckea crassifolia, Calytrix glaberrina and E. cneorifolia (Rawson et al., Reference Rawson, Davies, Whalen and MacKay2013).

Formation of aerial seed banks

Various species of Myrtaceae growing in fire-prone habits, e.g. in southwestern Australia (Lamont et al., Reference Lamont, Le Maitre, Cowling and Enright1991) retain seeds on the mother plant for extended periods of time (Table 9). Prolonged storage of viable seeds in the canopy is called serotiny, and it is more likely to be found in fire-killed, nonsprouting species than in species capable of resprouting after fire (Lamont et al., Reference Lamont, Le Maitre, Cowling and Enright1991, Reference Lamont, Pausas, He, Witkowski and Hanley2020). The seed-holding structures in serotinous Myrtaceae are woody capsules (Wellington and Noble, Reference Wellington and Noble1985) or infructescences of capsules (Whelan and Brown, Reference Whelan and Brown1998; Kim et al., Reference Kim, Walck, Hidayati, Merritt and Dixon2009). These capsules can provide some protection of seeds from the heat of fires (Judd and Ashton, Reference Judd and Ashton1991; Judd, Reference Judd1994; Whelan and Brown, Reference Whelan and Brown1998; Battersby et al., Reference Battersby, Wilmshurst, Curran and Perry2017b).

Table 9. Aerial seed bank (serotiny) in species of Myrtaceae

M-S, moderately to strongly serotinous; W, weakly serotinous; W-M, weakly to moderately serotinous; W-S, weakly to strongly serotinous; –, no information; mo, months; yr, years.

Aerial seed banks have advantages for the species, including protection of seeds from granivores on the soil surface such as ants, and the continuous supply of viable seeds although few or no seeds are produced in some years (Lamont and Enright, Reference Lamont and Enright2000). When the seeds are dispersed, they can germinate immediately because they are ND (e.g. Kim et al., Reference Kim, Walck, Hidayati, Merritt and Dixon2009). However, habitat substrate moisture and temperatures must be favourable for germination at the time of seed dispersal because seeds of serotinous species quickly lose viability on/in the soil (Cowling and Lamont, Reference Cowling and Lamont1987; Enright and Lamont, Reference Enright and Lamont1989), or they may be eaten by predators (Wellington and Noble, Reference Wellington and Noble1985).

In some serotinous species, capsules slowly open throughout the year, resulting in a low rate of seed dispersal, e.g. Eucalyptus luehmanniana (Tozer and Bradstock, Reference Tozer and Bradstock1997) and Melaleuca quinquenervia (Baumann and Hewitt, Reference Baumann and Hewitt2023). In fire-prone habitats in New Zealand, capsules of Leptospermum scoparium remain attached to the parent plant and do not open for 1 year or longer, but in other kinds of habitats capsules split and release the seeds within 1 year (Harris, Reference Harris2002). Mature fruits remain alive on plants of Callistemon rigida for 3–4 years or longer, but they die and open when their water supply is stopped (Ewart, Reference Ewart1907). Fruits of Melaleuca parvistaminea dried and opened when plants were cut (Jacobs et al., Reference Jacobs, Richardson and Wilson2014). In M. ericifolia, a wetland species, the peak of annual seed dispersal is in April, at which time water levels in the habitat are low (Hamilton-Brown et al., Reference Hamilton-Brown, Boon, Raulings, Morris and Robinson2009). Fire is an important and reliable seed-releasing factor because it promotes massive capsule opening and seeds are released into sites where fire has removed the standing vegetation (e.g. dos Santos et al., Reference dos Santos, Matias, Deus, Águas and Silva2015; Hewitt et al., Reference Hewitt, Holford, Renshaw, Stone and Morris2015), i.e. fire prepares a good seed bed (Lamont and Enright, Reference Lamont and Enright2000). However, if a fire occurs after seed dispersal, it kills seeds on the soil surface (dos Santos et al., Reference dos Santos, Matias, Deus, Águas and Silva2015).

Future challenges to maintain species richness of Myrtaceae

Invasive species of fungi

The fungus Austropuccinia psidii (syn. Puccinia psidii) was first identified on guava (Psidium guajava) in South America (Winter, Reference Winter1884), but it now has been found on plants of Myrtaceae growing in many countries, including Australia (Glen et al., Reference Glen, Alfenas, Zauza, Wingfield and Mohammed2007; Pegg et al., Reference Pegg, Taylor, Entwistle, Guymer, Giblin and Carnegie2017; Berthon et al., Reference Berthon, Esperon-Rodriguez, Beaumont, Carnegie and Leishman2018), Mexico (Esperón-Rodríguez et al., Reference Esperón-Rodríguez, Baumgartner, Beaumont, Berthon, Carnegie, Alfonzetti, Barrados and Leishman2018), New Caledonia (Giblin, Reference Giblin2013), New Zealand (Campbell et al., Reference Campbell, Beresford, Fizherbert, Cary-Smith and Turner2020; Jo et al., Reference Jo, Bellingham, McCarthy, Easdale, Padamsee, Wiser and Richardson2022), South Africa (Roux et al., Reference Roux, Greyling, Coutinho and Wingfield2013; Paap et al., Reference Paap, Santini, Rodas, Granados, Pecori and Wingfield2023), Southeast Asia (Fensham et al., Reference Fensham, Carnegie, Laffineu, Makinson, Pegg and Wills2020; Liu et al., Reference Liu, Liu and Li2024) and the USA in Florida and Hawaii (Marlatt and Kimbrough, Reference Marlatt and Kimbrough1979; Loope, Reference Loope2010). Many strains of A. psidii have been identified, and research is being conducted to determine which species of Myrtaceae are susceptible to them (Soewarto et al., Reference Soewarto, Somchit, du Plessis, Barnes, Granados, Wingfield, Shuey, Bartlett, Fraser, Scott, Miller, Waipara, Sutherland and Ganley2020). Also, germplasm conservation, i.e. seed banking, has been initiated in Australia as a pre-emptive strategy to conserve Myrtaceae species susceptible to damage or death due to attack by A. psidii (Dalziell et al., Reference Dalziell, Funnekotter, Barret, Martino, Shade, Stray and Merritt2024).

Austropuccinia psidii attacks young growing stems and leaves as well as fruits of many species of Myrtaceae, resulting in the death of the infected plant parts. In susceptible species of Myrtaceae, the fungus attacks and kills the regrowth of plants following die-back, prevents seed production and kills seedlings (Fensham et al., Reference Fensham, Colling-Wood and Radford-Smith2021). Myrtaceae growing in eastern and southern coastal areas as well as the northern tropical rainforests of Australia are at high risk for fungal infection. Berthon et al. (Reference Berthon, Esperon-Rodriguez, Beaumont, Carnegie and Leishman2018) estimated that under current climate conditions in eastern and northern Australia, 1285 species of Myrtaceae are at risk of being exposed to A. psidii. As early as 2007, tests showed that 73 of 83 native species in 16 of 19 genera of Australian Myrtaceae are susceptible to A. psidii (Glen et al., Reference Glen, Alfenas, Zauza, Wingfield and Mohammed2007), and Fernandez-Winzer et al. (Reference Fernandez-Winzer, Verthon, Entwistle, Manea, Winzer, Pegg, Carnegie and Leishman2020) noted that the host range is 370 species of Myrtaceae.

Conditions for germination of spores of A. psidii are high humidity (or wetness), light for at least 6 h and warm temperatures (optimum of 25–28°C) (Campbell et al., Reference Campbell, Beresford, Fizherbert, Cary-Smith and Turner2020). Thus, it was hoped that in cool climates, e.g. New Zealand (Campbell et al., Reference Campbell, Beresford, Fizherbert, Cary-Smith and Turner2020), and dry climates, e.g. Western Australia (Berthon et al., Reference Berthon, Esperon-Rodriguez, Beaumont, Carnegie and Leishman2018), there is a reduced risk of Myrtaceae being infected by A. psidii. However, this fungus has been detected in the northern part of Western Australia (Dalziell et al., Reference Dalziell, Funnekotter, Barret, Martino, Shade, Stray and Merritt2024). Much concern is being expressed about global warming and the increased spread of A. psidii in places such as New Zealand (Jo et al., Reference Jo, Bellingham, McCarthy, Easdale, Padamsee, Wiser and Richardson2022), where climate warming could increase temperature enough to be favourable for the germination of A. psidii spores (Campbell et al., Reference Campbell, Beresford, Fizherbert, Cary-Smith and Turner2020). Unfortunately, A. psidii now has invaded the North Island of New Zealand, and 24 Myrtaceae species have been infected by it (Toome-Heller et al., Reference Toome-Heller, Ho, Ganley, Elliott, Quinn, Pearson and Alexander2020).

Due to repeated attacks by A. psidii on the regrowth of new stems and leaves, plants may die in 3–4 years, and some Myrtaceae in Australia, e.g. Archirhodomyrtus beckleri, Decaspermum humile, Gossia hillii and Rhodamnia maideniana, are in serious decline (Pegg et al., Reference Pegg, Taylor, Entwistle, Guymer, Giblin and Carnegie2017). Species such as Rhodamnia rubescens and Rhodomyrtus psidioides (Carnegie et al., Reference Carnegie, Kathuria, Pegg, Entwistle, Nagel and Giblin2016; Fernandez-Winzer et al., Reference Fernandez-Winzer, Verthon, Entwistle, Manea, Winzer, Pegg, Carnegie and Leishman2020) in Australia, Eugenia koolauensis in Hawaii (USA) (Loope, Reference Loope2010) and E. gacognei in New Caledonia (Fensham et al., Reference Fensham, Carnegie, Laffineu, Makinson, Pegg and Wills2020) are seriously threatened with extinction. Overall, the death of Myrtaceous species due to attack by A. psidii is affecting the structure of various plant communities in Australia, including wet sclerophyllous forests, rainforests, wetlands and swamps (Glen et al., Reference Glen, Alfenas, Zauza, Wingfield and Mohammed2007; Carnegie et al., Reference Carnegie, Kathuria, Pegg, Entwistle, Nagel and Giblin2016; Pegg et al., Reference Pegg, Taylor, Entwistle, Guymer, Giblin and Carnegie2017; Fernandez-Winzer et al., Reference Fernandez-Winzer, Verthon, Entwistle, Manea, Winzer, Pegg, Carnegie and Leishman2020). Other invasive fungi such as Phytophthora cinnamoni (Carnegie et al., Reference Carnegie, Kathuria, Pegg, Entwistle, Nagel and Giblin2016; Fensham et al., Reference Fensham, Carnegie, Laffineu, Makinson, Pegg and Wills2020; McDougall and Liew, Reference McDougall and Liew2024; McDougall et al., Reference McDougall, Barrett, Velzeboer, Cahill and Rudman2024) cause die-back and death of Myrtaceae species. Also, the polyphagous short-hole borer/beetle Euwallacea fornicatus and its associated fungus Fusarium sp., which can lead to tree death, have been detected in Western Australia, and many Myrtaceae species can serve as hosts (Dalziell et al., Reference Dalziell, Funnekotter, Barret, Martino, Shade, Stray and Merritt2024).

In the Hawaiian Islands, the vascular wilt fungi Ceratocystis lukuohia and the canker pathogen C. huliohia have caused the death of many Metrosideros polymorpha trees (Camp et al., Reference Camp, LaPointe, Hart, Sedgwick and Canale2019; Atkinson and Roy, Reference Atkinson and Roy2023). Not only do the dying trees have a significant impact on forest structure, but this loss of trees has major negative effects on the native birds that depend on the flowers of M. polymorpha for food (Camp et al., Reference Camp, LaPointe, Hart, Sedgwick and Canale2019).

Other challenges and some possible solutions

The ever-increasing effects of human activities on natural ecosystems, in particular the destruction of natural habitats of species of Myrtaceae, are causing many species to become rare and in some cases on the verge of extinction (Breman et al., Reference Breman, Ballesteros, Castillo-Lorenzo, Cockel, Dickie, Faruk, O'Donnell, Offord, Pironon, Sharrock and Ulian2021). In addition to the potential loss of Myrtaceae species and their habitats, the animals in these habitats that use Myrtaceae species as food will be negatively affected, e.g. tropical dry forests in the Andes Mountains (Galván-Cisneros et al., Reference Galván-Cisneros, Montaño, Ojeda-Rodriguez and Maira-Neto2023). These authors note that with the loss of animals seed dispersal across the landscape will be decreased, thereby reducing the regeneration of Myrtaceae species from seeds and restricting the distribution of species.

In addition to habitat destruction and loss of seed dispersal, global warming with increased temperatures and modified patterns of precipitation could intensify the negative effects of increased fire intensity and frequency in plant communities dominated by species of Myrtaceae and promote the spread of pathogenic fungi that can kill plants of Myrtaceae. The challenge for the future is to find ways to conserve species of Myrtaceae (and other plant families) that are being threatened with extinction.

Growing plants in botanical gardens (Breman et al., Reference Breman, Ballesteros, Castillo-Lorenzo, Cockel, Dickie, Faruk, O'Donnell, Offord, Pironon, Sharrock and Ulian2021) and storing seeds in seed banks (e.g. Pilatti et al., Reference Pilatti, Aguiar, Simões, Benson and Viana2011; Hardstaff et al., Reference Hardstaff, Sommerville, Funnekotter, Bunn and Offord2022) are two conservation options. However, seeds of some Myrtaceae are desiccation-sensitive and can not be stored dry at low temperatures. Thus, cryogenic techniques for storage are being tested/used for pollen, seeds, embryos and shoot tips of Myrtaceae (Kaczmarczyk et al., Reference Kaczmarczyk, Turner, Bunn, Mancera and Dixon2011; Nadarajan et al., Reference Nadarajan, van der Walt, Lehnebach, Saeiahagh and Pathirana2021). More conservation areas/preserves are needed to protect the habitat and species, e.g. in the Brazilian Cerrado (Oliveira et al., Reference Oliveira, Staggemeier, Faria, Oliveira and Diniz-Filho2019) and the Atlantic Forest of eastern Brazil (Oliveira et al., Reference Oliveira, Gasper and Vibrans2021). Also, methods to propagate critically endangered species, especially from seeds, are needed (e.g. Sarcar et al., Reference Sarcar, Sarcar and Chelladurai2006; Montalyo et al., Reference Montalyo, Quiala, Matos, Morffi, de Feria, Chávez, Balbõn and Pérez2010; Raju et al., Reference Raju, Krishna and Chandra2014).

One idea for conserving rare species of Myrtaceae, especially in Australia where some species are becoming rare due to fungal attack (Fensham et al., Reference Fensham, Colling-Wood and Radford-Smith2021) is to grow plants in regions where the climate is not suitable for the fungi. For example, growing species of Myrtaceae in locations with <900 mm annual precipitation potentially would prevent the plants from being attacked by A. psidii (Fensham et al., Reference Fensham, Carnegie, Laffineu, Makinson, Pegg and Wills2020). However, when growing species of Myrtaceae in new habitats, consideration needs to be given to edaphic factors such as acidity and fertility (Gomes et al., Reference Gomes, Stedille, Milani, Montibeller-Silva, Costa, Gatiboni, Montovani and Bortoluzzi2020).

Another possibility for conserving species of Myrtaceae threatened by A. psidii is to breed/select for resistance to pathogenic fungi (Chock, Reference Chock2020; Smith et al., Reference Smith, Ganley, Changé, Nadarajan, Pathairana, Ryan, Arnst, Sutherland, Soewarto, Houliston, March, Koot, Carnegie, Menzies, Lee, Shuey and Pegg2020; Yong et al., Reference Yong, Ades, Runa, Bossinger, Sandhu, Potts and Tibbits2021). Further, a spray containing double-stranded RNA from A. psidii has shown effectiveness in both preventing and curing infection by A. psidii on Syzygium jambos trees (Degnan et al., Reference Degnan, Shuey, Radford-Smith, Gardiner, Carroll, Mitter, McTaggart and Sawyer2023).

Concluding thoughts

In our comparison of the highly speciose, widely distributed plant families, the Asteraceae, Rubiaceae and Myrtaceae, which are the first, fourth and ninth most speciose angiosperm families, respectively (Mabberley, Reference Mabberley2017), have been considered. The Asteraceae has trees, shrubs, lianas and herbs, with number of life forms decreasing with distance from the Equator, resulting in only herbs in the tundra (Baskin and Baskin, Reference Baskin and Baskin2023). Only one kind of embryo (spatulate) is found in cypselae (seeds) of Asteraceae, and seeds may be ND or have PD. The six known types of nondeep PD occur in the Asteraceae, and, depending on habitat/vegetation region, PD is broken by warm summer or cold moist winter conditions. Thus, in Asteraceae, the great species richness is related to seed dormancy-breaking and germination requirements that closely coincide with a wide range of habitats throughout the world, except Antarctica.

The Rubiaceae has trees, shrubs, lianas/climbers and herbs. The highest species richness is in moist tropical forests, but some shrubs and herbs grow in temperate regions and a few herbs in the tundra. The Rubiaceae has five kinds of embryos, and seeds are ND or have morphological, physiological or morphophysiological dormancy. The greatest species richness in Rubiaceae is related to the diversity of seed dormancy, especially among tropical rainforest trees and semi-evergreen rainforest shrubs (Baskin and Baskin, Reference Baskin and Baskin2024).

The Myrtaceae has only trees, shrubs and a few viny epiphytes but no herbs. The distribution of the family outside the tropics is in regions with a Mediterranean climate, e.g. Australia, South Africa and southern Europe/North Africa, and to a limited extent in temperate vegetation regions such as broad-leaved evergreen forests and grasslands. Five kinds of fully developed embryos are found in seeds of Myrtaceae; however, seeds are either ND or have PD, regardless of tribe, habitat/vegetation region or kind of fruit produced. Great species richness is found in fleshy-fruited Myrtaceae that grow in moist tropical regions. Seeds of fleshy-fruited species are either ND or have PD that is broken during exposure to relatively high temperatures, after which seeds germinate at high temperatures. The only known exception is for seeds of fleshy-fruited Myrtus communis that become ND during cold stratification. However, after cold stratification, seeds germinated to high percentages at 25–30°C than at 10–20°C (Benvenuti and Macchia, Reference Benvenuti and Macchia2001). Also, seeds of Baeckea utilis buried in the subalpine of the Brindabella Mountains (Australian Alps) in southeastern Australia germinated to higher percentages when exhumed in spring (3, 12 and 27 months of burial) than those exhumed in winter or autumn (6, 9 and 21 months of burial) (Guja and Brindley, Reference Guja and Brindley2017). These results suggest that cold stratification during winter was breaking seed dormancy.

Great species richness is also found in dry-fruited Myrtaceae species that grow in seasonally dry tropical vegetation regions and in habitats with a Mediterranean climate, e.g. the matorral with hot, dry summer and cool, moist winters. For dry-fruited species, dormancy-break during the hot, dry season is followed by germination when the wet season begins. In tropical vegetation regions, temperatures are high when the wet season begins; thus, both dormancy-break and germination occur at high temperatures. In the matorral, seeds germinate over a range of low to high temperatures that include the temperatures (e.g. c. 15°C) of the cool, rainy season. Thus, in the Myrtaceae, we find many fleshy-fruited species in which both seed dormancy-break and germination occur during exposure to warm, wet conditions (e.g. rainforest) and many dry-fruited species in which dormancy-break at warm, dry conditions are followed by germination at either warm, wet (e.g. savannas) or cool-to-warm, wet (e.g. matorral) conditions.

Supplementary material

To view supplementary material for this article, please visit: https://doi.org/10.1017/S0960258525000066.

Competing interests

The authors have no conflict to declare.

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Figure 0

Figure 1. Embryo types of Myrtaceae. (A) Linear-full (myrtoid); (B) spatulate; (C) bent; (D) folded (myrcioid) and (E) investing (eugenioid). A, axis (which is covered by cotyledons); C, cotyledons; H, hypocotyl.

Figure 1

Table 1. Number of genera with different kinds of embryos in each tribe of Myrtaceae and occurrence of nondormancy (ND) and physiological dormancy (PD) in each tribe

Figure 2

Table 2. Seed dormancy profile for trees and shrubs of Myrtaceae in different vegetation regions

Figure 3

Table 3. Tribes of Myrtaceae, vegetation regions (1–9)a and life form (tree or shrub)

Figure 4

Table 4. Species of Myrtaceae with desiccation-sensitive (recalcitrant [R] or intermediate [I]) seed storage behaviour

Figure 5

Table 5. Effect of dry heat treatments on seed germination of species of Myrtaceae

Figure 6

Table 6. Effect of smoke and/or smoke extracts on seed germination of species of Myrtaceae

Figure 7

Table 7. Soil seed bank of Myrtaceae

Figure 8

Table 8. Longevity of seeds of Myrtaceae placed in mesh bags and buried in soil in the field

Figure 9

Table 9. Aerial seed bank (serotiny) in species of Myrtaceae

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