1. Introduction
Maples (
Acer sp.) are popular landscape trees often identified by commonly having palmately lobed leaves and characteristic schizocarps (joined samaras). However, many species differ from the archetype palmately lobed leaves and most species are not particularly desired for their flowers or fruit, though few exceptions exist (e.g., ‘Flame’ amur maple grown for its red schizocarps). In 2014, overall U.S. sales of maples exceeded
$173 million, which accounted for 31% of the nearly
$562 million of deciduous shade trees sold nationally [
1]. Much of the nursery stock produced around the country is marketed to population centers in the upper Midwest and New England regions. In fact, Oregon, the leading shade tree production state in the U.S., ships approximately 80% of its nursery plant material out of state and historically has relied on regions in the eastern part of the U.S. as principle markets.
With the nearly complete loss of elms and ash from the market due to Dutch elm disease [
2] and emerald ash borer [
3], respectively, the nursery and landscape industries are more reliant on maples to fill the urban canopy. However, many maples have the significant drawback of being weedy. Several species have escaped cultivation and become invasive to the point of being banned in some states, which has resulted in a significant decline of staple species in historically key markets such as New England.
Among the most widely used maples, Norway maple (A. platanoides) became popular in the U.S. in the mid- to late-1800s and continues to be widely used as a street and shade tree. Following previous devastating losses of elm trees from Dutch elm disease, large numbers of Norway maples were planted. Desirable forms include columnar growth habit, red leaves, and cultivars with improved fall color. Norway maples grow well under a wide range of conditions including sand to clay and acid to calcareous soils. It is hardy from USDA Zone 4 to 7 and tolerates hot, dry conditions better than sugar maple. Furthermore, Norway maple is tolerant of air pollution, including ozone and sulfur dioxide, making it ideal for use as a street tree. However, a major problem with Norway maple is that it has become naturalized to the point of invasiveness in forests of New England. Between 2009 and 2014, sales of Norway maple fell by more than 5% from $14.4 million to $13.6 million but many growers have seen much more dramatic declines in sales. Based on conversations with leading shade tree growers, this downward trend continues. Robinson Nursery, an Oregon shade tree grower, estimates their market is down 90% from a decade ago. Their data indicates they sold approximately 25,000 Norway maples annually between 2000 and 2006, but today they sell closer to 3000. It is likely that a continued downward trend will be observed unless alternative cultivars are introduced.
Other street trees that previously were dominant in the market have seen precipitous declines in sales due to emerging pests. Ash (
Fraxinus spp.) was a leading street tree until recently; however, with the emergence of emerald ash borer as a major pest, the viability of ash as a commercial crop has been reduced. Sales declined from nearly
$15 million in 2009 to less than
$10 million in 2014 [
1] and the pest continues to devastate the Midwestern urban tree canopy, thus one would expect ash sales to continue to fall. Since currently there is not a viable source of resistance in the U.S., it is imperative we have alternatives in the nursery and landscape industry to replace street trees in American cities.
Ecological and economic harm occurs when ornamental plants escape cultivation and displace native flora, which requires costly action on the part of land managers [
4]. Furthermore, legislation preventing nurseries from producing and selling these species causes economic harm to growers. The fruit (winged samaras or schizocarps) that are so well recognized in the landscape are also notorious for introducing unwanted maple seedlings into both the urban and natural landscapes. Currently, there are three maples species [
Acer tataricum ssp.
ginnala (Amur maple),
A. platanoides,
A. pseudoplatanus (sycamore maple)] listed as noxious weeds in Connecticut and Massachusetts. Of these three species, two are banned from the state of Massachusetts and one is banned in Connecticut [
5]. While not yet listed in other regions of the country, these species are widely distributed and have naturalized over large areas (
Figure 1). Norway maple is extremely shade tolerant and its phenology is such that it releases its seeds at an appropriate time for survival (early fall) and natural cold stratification. This is in contrast to red maple (
A. rubrum), for example, that has mature schizocarps during summer when summer drought often prevents recalcitrant seeds from surviving.
Species listed as “maple, other” accounted for more than
$32 million in sales during 2014 [
1]. This is important to note because many of these other species produce copious amounts of viable seed that have the potential to escape cultivation and create similar ecological issues as Norway and Amur maple. It is worth noting that Norway maple was introduced into the U.S. around 1756 [
6] and there was a lag phase before populations reached levels sufficient to cause ecological harm. It is reasonable to predict that with time; other species of maples have the potential to spread from cultivation. They, too, could become noxious weeds and eventually be banned from production or sale. As such, the methods and results described herein have application in other maple species.
Fertility of weedy species can be reduced using a number of techniques including ploidy manipulation. Other more technical methods such as gene editing and transgenics are far more expensive, require intimate knowledge of genomes of interest, and regeneration systems to recover whole plants from in vitro transgenic cell lines [
7], all of which are generally lacking for maples. Furthermore, negative public perception and the cost of navigating regulatory approval is estimated to be in the tens of millions of dollars [
8]. Ploidy manipulation to develop sterile triploids is relatively inexpensive and proven effective in many plant taxa. Inducing polyploids using chemical means, particularly the dinitroaniline herbicide, oryzalin, has become commonplace in woody plants including
Acer [
9,
10,
11]. Ploidy is the number of chromosome sets found in an organism and most organisms have two sets (diploids = 2
x) but plants are capable of existing with more than two sets of chromosomes. Plants can be rendered sterile, or at least have their fertility reduced, by producing cultivars with an odd number of chromosome sets—most commonly three sets (i.e., triploids = 3
x) [
12]. Sterility resulting from triploidy occurs because plants with an odd ploidy number cannot be equally divided during meiosis such that daughter cells contain between
n and
2n chromosomes [
13]. In most cases where rare seedlings do arise from triploids, they often are aneuploids with reduced fitness and pose little or no ecological threat to escape cultivation [
14]. This is a longstanding and common technique that resulted in seedless food crops such as bananas [
15], watermelons [
16], and some cultivars of grapes [
17]. In nature, triploids can occur through production of unreduced (2
n) gametes [
14]. However, plant breeders can double the chromosomes of a diploid plant using various chemicals and the resulting tetraploid (4
x) plant is then crossed with the diploid plant to create triploids. Induced polyploidy has been used in a wide variety of woody plants [
7]. However, fewer examples are found for woody ornamentals. Lehrer et al. (2008) developed tetraploids of Japanese barberry (
Berberis thunbergii), a weedy species in New England [
18]. Their use of ploidy manipulation resulted in plants later released as ‘UCONNBTCP4N’ USPP 30,095 Crimson Cutie
® and ‘UCONNBTB048’ USPP 30,127 Lemon Glow
® barberry. These examples are interesting, as they were found to be nearly sterile at the autotetraploid level, presumably due to multivalent formation, which avoided the need to proceed to the next generation. Rounsaville et al. (2011) compared fertility of diploid to triploid cytotypes of maidengrass (
Miscanthus sinensis) and found the latter to have as low as 0.7% fertility relative to the wild type [
19]. Phillips et al. (2016) developed triploid flowering pears (
Pyrus sp.) that ranged from 0% to 34% relative fertility compared to diploid controls—a study that highlights the need for extensive and thorough testing of resulting triploids [
20].
Campsis ×
tagliabuana ‘Chastity’ is a triploid cultivar of trumpet creeper that was developed by crossing a diploid cultivar with an oryzalin-induced tetraploid that is reported to have >99% reduction in fertility compared to diploid
C. radicans [
21].
Maples generally are diploids with two copies of 13 base chromosomes (2n = 2x = 26). To address the issue of weediness among maples, we developed triploids (3x = 39) that we hoped would exhibit reduced fertility and thus lessen the potential negative impacts of weedy and potentially invasive maple species. Introducing cultivars of maple with reduced fertility would allow land managers to maintain ecologically well-adapted species that thrive in difficult urban environments. Cultivars with reduced fertility would support the urban forests where they are planted and also protect the surrounding natural environments by preventing escape from cultivation. Furthermore, such cultivars support the sustainability of nursery producers who have relied heavily on these economically important species but have suffered due to the decline in demand as a result of their weediness. To address the need for sterile maple cultivars, the objectives of the current research were to (1) develop tetraploids (2) backcross to diploids to produce triploids and (3) evaluate fertility as plants began flowering to determine if triploid maples exhibit reduced fertility. While we discuss the methods used to generate tetraploids, we do not consider these necessarily to be optimized methods.
4. Discussion
Norway and Amur maples are important nursery and landscape species that have declined in sales due to their invasiveness. Previous research has attempted to address this by identifying existing cultivars of Norway maple that have reduced fertility [
22]. Conklin and Sellmer [
22] observed low to moderate germination during their study even though many of the cultivars studied are known to be relatively weedy but conceded that even though recommended methods for overcoming dormancy were followed, there may have been confounding factors. We have observed delayed germination of some Norway maple genotypes that required longer cold stratification than commonly recommended for the species. Additional observations related to flowering and seed set resulted in the conclusion that some cultivars such as Crimson King, Globosum, Faasen’s Black, and Rubrum had relatively low seed set and were safe alternatives for landscapes [
23]. Our observations of several of these cultivars in Western Oregon, particularly for Crimson King, have found that they are not reduced in fertility. Conflicting observations from different climatic regions points toward an environmental factor in fertility. This idea of safety among existing Norway maple cultivars has been propagated by others through citation of the Conklin and Sellmer research and also refers to newer cultivars that were developed for use in eastern North America such as ‘Medzam’ (Medallion™) as “virtually-seedless” [
24] but it is unclear on what basis that claim was made other than that of the nursery that introduced the cultivar. These assertions of reduced fertility without sufficient evidence may have an impact on future releases of sterile cultivars. Touting plants as sterile that have either not been properly evaluated or have not flowered may prevent any future exceptions to be made following bans and/or could jeopardize acceptance among the public, who may rightly view such cultivars with skepticism. Indeed, even when there is a scientific basis for a plant that “should” have reduced fertility (e.g., triploidy), testing is still required. For instance, among 13 populations of triploid pears, Phillips et al. [
20] observed 0% to 33% fertility compared to a fertile diploid control, which illustrated a genetic factor related to fertility.
To provide sterile cultivars for growers and land managers that will not escape cultivation we first successfully induced tetraploids by treating the meristem of newly germinated seedlings. This technique has been widely used across diverse taxa including
Hibiscus acetosella [
25] and
Rhododendron [
26], whereas other research used in vitro treatment to develop tetraploids to maintain the phenotype of ‘Crimson Sentry’ [
27]. We were not successful in developing tetraploids by treating vegetative meristems in situ and thus if future researchers wish to use cultivars to maintain superior phenotypes, it is recommended to follow a similar protocol to Lattier et al. [
27], which focused on in vitro treatment. Similar to previous research, we observed varying percentage of tetraploids and cytochimeras both within and among species. We did not further investigate the resulting mixoploids to determine LI and LIII histogenic layers through stomatal measurements (LI) or observations related to adventitious roots (LIII) as performed on
Hibiscus acetosella [
25]; however, we did retain all mixoploids due to the potential that they may be more precocious to flower and would breed as tetraploids based on the ploidy of LII. Additionally, we confirmed one cytochimera of Amur maple to be an LII tetraploid based on pollen size. Utility of cytochimeras to breed as tetraploids has been illustrated in other taxa such as the bigeneric hybrid x
Chitalpa [
28]. However, due to the relative number of tetraploids in the current study and the precocity of flowering among them, we have not relied heavily on them for breeding. Cytochimeras in our program continue to exhibit variable ploidy levels including some stabilizing as diploids, others as tetraploids, and some maintaining as chimeras. Among chimeras we have confirmed individual branches varying in ploidy level, which requires testing ploidy level each year during flowering. Annual confirmation of ploidy of plants from which we collect seed has become our standard practice to ensure efficiency through sowing only populations of seed that will yield high percentage of triploids.
Other researchers have used non-targeted mutagenesis to develop sterile forms of Amur maple and observed that several selections had not flowered or produced seed for several years [
29]. While sterility or reduced fertility is a common result following mutagenesis using radiation (e.g., ‘Meiguicheng’ orange [
30]), the authors conceded that the treatment may simply have resulted in the non-flowering plants having a longer than typical juvenility period. In order to have the greatest assurance that plants will not set seed is to observe flowering in many environments in the presence of fertile pollinizers over many years. We chose to use ploidy manipulation, as developing triploid cytotypes has been demonstrated to be a reliable means to achieve greatly reduced fertility in woody landscape plants such as
Campsis [
21],
Hypericum [
31], and
Pyrus [
20].
To our knowledge, these are the first confirmed reports of triploid forms of Amur, Norway, or trident maples developed to date. After attempting interploidy crosses using hand pollination we found that the process was inefficient and resulted in relatively few seedlings. We opted to interplant diploids and tetraploids to allow open-pollination. Prior to planting we were not certain of the pollination syndromes of any of the three species. There are five breeding systems in the genus
Acer, several of which are highly complex and variably expressed temporally but can be summarized to range from including perfect flowers to dioecy during a single season [
32]. Norway maple has been referred to as having perfect flowers [
33] but this is a miscategorization, and even making careful observations can result in erroneous conclusions if based on a single period of time, as flowers can shift from perfect to male or female. We have made seasonal observations over the past several years but have not conducted observations on the frequency required to resolve sex expression these three species. However, we have confirmed the presence of perfect and male flowers in both Amur and Norway maples. Regardless of sex expression and/or pollination syndrome, the relatively high percentage of triploids derived from tetraploid plants suggests that there is a high rate of outcrossing among the maples studied.
Thus far we have observed triploids of Amur maple flowering for three seasons and have not recovered any seedlings, even though there are fertile pollinizers interplanted. All plants that flowered initially set samaras but all desiccated prior to maturation. Nevertheless, we collected, stratified, and sowed these seeds and observed no germination. It is premature to refer to these plants as sterile, but the findings suggest these plants may have reduced fertility to remove the ecological threat presented by the species-type. Triploids of Amur, Norway, and trident maples all have been propagated by stem cuttings for evaluation in multiple locations over multiple years.