Abstract
In 2017, Mt. Cuba Center completed a survey that assessed the diversity of plants grown by mid-Atlantic wholesale nurseries. The main objectives were to quantify the proportion of taxa (named entities) native to the Eastern Temperate Forest Eco-region (those generally marketed as native in the regional horticulture industry), as well as the number of taxa considered invasive in the mid-Atlantic. Results indicated that 25% of the total 6885 taxa are either species native to the Eastern Temperate Forest or cultivars and hybrids of those species. The vast majority of that group (77%) belong to the latter categories of cultivars and hybrids. The taxa sold through these regional nurseries represent 1368 species. Of those, 458 (33%) represent species native to the Eastern Temperate Forest. Taxa considered invasive in the mid-Atlantic region represented 4% of the total diversity. This assessment represents the first of its kind in the mid-Atlantic and will serve to inform interested parties about the current state of native and invasive plants in this region.
Native plants are increasingly recognized as a desirable component of the built landscape. Horticulture professionals are aware that these plants can provide ornamental as well as functional value. The ability to provide important ecosystem services is also making native plants increasingly relevant to home gardeners. This growing awareness among professionals and hobbyists alike has resulted in an increased demand for native plants. One of the most often-heard complaints regarding the use of natives, however, is that they are not widely available (Brzuszek and others 2007, 2010; Brzuszek and Harkess 2009).
Native plants in built landscapes provide important benefits to the natural world, whereas non-native, invasive plants currently pose a significant threat to natural ecosystems (Pimental and others 2005). Many invasive plants were first introduced for horticultural purposes (Reichard and White 2001). Lehan and others (2013) confirmed this when their study found that 60% of the invasive species in the US were introduced deliberately, and the majority of those (64%) were for ornamental purposes. Although their invasive nature was not known at the time of introduction, these plants are now displacing naturally occurring plant communities. Disturbed and fragmented landscapes are particularly vulnerable to invasion (Dix and others 2009), which makes invasive plants an acute concern in the highly developed mid-Atlantic region.
Despite the growing awareness of both native and invasive plants, information is limited regarding their prevalence in the mid-Atlantic horticulture industry. To better quantify these trends, Mt. Cuba Center conducted an assessment of leading wholesale growers in several mid-Atlantic states in 2016–2017 to provide a current accounting of the taxa being sold and to determine how many of those are native or invasive.
MATERIALS AND METHODS
A group of 14 wholesale nurseries were strategically chosen to best represent the horticultural plant taxa sold throughout the entire mid-Atlantic region. For the purpose of this study, the mid-Atlantic region was defined as the following states: New York, Pennsylvania, New Jersey, Delaware, Maryland, and Virginia. This survey focused on growers of hardy plants (those that persist year after year), as relatively few horticultural annuals are native or invasive. Retail outlets were not surveyed because of a lack of product lists and because the taxa they sell would be included in the lists from wholesale nurseries.
The nurseries included in this survey represent medium- to large-sized businesses that are based in the mid-Atlantic and that ship plants throughout the region. These nurseries were chosen because of their extensive plant offerings and their likeliness to continue in business for the coming decades, thus facilitating repeat assessments. Nurseries were also specifically chosen to include a diverse mix of plant forms (trees, shrubs, perennials, and so forth) and growing methods (container and field production). Table 1 provides a profile of each nursery including location, growing method, and products sold. Together these 14 nurseries well represent the hardy plants grown for horticultural purposes throughout the mid-Atlantic.
Product lists were gathered from each nursery and entered into Microsoft Excel (2016, Microsoft Corporation, Redmond, Washington). Many nurseries were inconsistent in their taxonomy or spelling for the same taxon. Therefore, taxa names required significant editing to normalize discrepancies prior to classification and analysis. Once normalized, reference books by Armitage (2008) and Dirr (2009), as well as the Biota of North America Program (BONAP), the Missouri Botanical Garden (MOBOT) Plant Finder, the Center for Invasive Species and Ecosystem Health, and the USDA PLANTS online databases were used to categorize each taxon based on several subjects. These included nativity, invasiveness, and plant form. These classifications are further defined below.
In this study, a species was categorized as native if it is known to naturally occur within the Eastern Temperate Forest Ecoregion (Omernik 1987). The USDA PLANTS and BONAP databases were used to determine whether a species occurs in the Eastern Temperate Forest Ecoregion. This boundary is admittedly much broader than the mid-Atlantic region surveyed; however, it is the author’s observation that most growers, retailers, and horticulturists in the mid-Atlantic region ascribe the term “native” to the relative geographic area of the eastern US. Since that area does not have explicit boundaries, the Eastern Temperate Forest Ecoregion (ETF) is a more precisely delineated approximation of that geographic range.
Cultivars of species native to the Eastern Temperate Forest were designated as a category separate from native species. In this study, cultivars are defined narrowly to exclude hybrids, which were given a separate category. This approach is a departure from traditional horticulture terminology that technically includes hybrids as a type of cultivar. Our definition includes only taxa that are directly selected from a species native to the ETF. These are often colloquially referred to as “selections,” but that term has no official meaning in the International Code of Nomenclature for Cultivated Plants (2016).
Hybrids of species and cultivars native to the ETF were given their own designation as well. It is important to recognize that nearly all of these hybrids are not naturally occurring; rather, they are derived from direct human intervention and thus should not technically be considered native. Despite this inaccuracy, it is common to see such hybrids lumped in the native category as a horticultural convention, so this category was created to capture those taxa. Another important caveat with assigning nativity to a hybrid taxon is that it is often impossible to know the entire breeding lineage. Therefore, while the taxa in this category are believed to have at least one parent native to the ETF, it is usually not possible to know the full lineage of these plants.
Invasiveness was categorized based on the online database of Invasive and Exotic Species Profiles & State, Regional, and National Lists compiled by Invasive.org, which is a collaborative project between the National Park Service, the University of Georgia Center for Invasive Species and Ecosystem Health, the Invasive Plant Atlas of New England, and the Lady Bird Johnson Wildflower Center. Unfortunately, no universally accepted invasive plant list is available for the entire mid-Atlantic region. Invasive.org does aggregate various state and regional lists into one database. We categorized plants listed as invasive in the states of New York, Pennsylvania, New Jersey, Delaware, Maryland, and Virginia as such in this study.
We also classified all taxa by plant form to provide more detailed analysis. Plant forms were designated based on common horticultural categories and include annual, perennial, graminoid, fern, vine, bamboo, shrub, tree, and edible. The distinction between tree and shrub is somewhat subjective, so we used a mature height breakpoint of 4.5 to 6 m (15–20 ft). Plants taller than this range would be considered trees and shorter plants categorized as shrubs. One exception to this rule was that all Japanese maples (Acer palmatum Thunb. [Aceraceae]) were categorized as trees even if their mature height was shorter than 4.5 m. The edible category also includes plants that could be placed under other categories such as annual, tree, or vine.
However, we decided to group all plants primarily grown for food consumption rather than ornamental purposes into one category.
RESULTS AND DISCUSSION
The surveyed mid-Atlantic nurseries sell 6885 different taxa. Table 2 provides the breakdown of taxa by plant type, nativity, and invasiveness. Overall, perennials make up the largest plant group with 48% of all taxa, followed by shrubs (23%), trees (10%), annuals (5%), edibles (5%), graminoids (5%), vines (3%), ferns (1%), and bamboo (<1%).
Native Plants
Of the taxa grown by the surveyed nurseries, 1701 (25% of all taxa) were identified as native to the Eastern Temperate Forest Ecoregion or derived from such natives (Table 2). This included ETF native species, cultivars of those species, as well as their related hybrids. Further dissection revealed 391 taxa (6% of all taxa) were species native to the Eastern Temperate Forest, 791 taxa (11% of all taxa) were cultivars of ETF species, and 519 taxa (8% of all taxa) were hybrids of ETF species and cultivars. These measures of overall taxa diversity can be somewhat misleading though because a handful of genera provided a disproportionate number of taxa as cultivars and hybrids. In fact, just 5 genera (Heuchera L. [alumroot, Saxifragaceae], Phlox L. [phlox, Polemoniaceae], Echinacea Moench [purple coneflower, Asteraceae], Coreopsis L. [tickseed, Asteraceae], and Hibiscus L. [rosemallow, Malvaceae]) accounted for 50% of the diversity of all native perennial taxa. A similar situation occurred with shrubs, in which 5 genera (Vaccinium L. [blueberry, Ericaceae], Ilex L. [holly, Aquifoliaceae], Thuja L. [arborvitae, Cupressaceae], Hydrangea L. [hydrangea, Hydrangeaceae], and Rhododendron L. [rhododendron, Ericaceae]) accounted for 42% of all native shrub taxa. In trees, 5 genera (Cercis L. [redbud, Fabaceae], Ilex L. [holly, Aquifoliaceae], Magnolia L. [magnolia, Magnoliaceae], Acer L. [maple, Aceraceae] and Quercus L. [oak, Fagaceae]) accounted for 38% of all native taxa. Native graminoid and fern taxa also belonged to relatively few genera; however, these were mainly species-rich genera and were not as heavily affected by an abundance of cultivars and hybrids.
One way of analyzing nativity without these distorting effects is by species representation (see Table 2). Many species were represented only as cultivars, thus both species and cultivars were analyzed together. Of the 1368 species represented in the survey, ETF native species comprised 458 (33%). The reason for such a dramatic difference between the analysis by taxa and analysis by species representation is largely caused by hybrid taxa. These have no attributable species and occurred most frequently as non-natives in the genera Rosa L. (rose, Rosaceae), Hosta Tratt. (plantain lily, Liliaceae), Clematis L. (leather flower, Ranunculaceae), Hemerocallis L. (daylily, Liliaceae), and Rhododendron L. (rhododendron, Ericaceae). These 5 genera alone accounted for 1396 hybrid taxa, which was 20% of the entire survey. This high proportion of non-native hybrids greatly skewed the percentage of taxa toward non-natives.
However, analysis by species representation is not perfect either as the ecological value of cultivars of native plants is a topic of frequent debate. Early scientific and anecdotal research demonstrates that many, though not all, cultivars are able to provide ecosystem services on par with, and in some cases better than, the native species from which they are derived (Coombs 2016, 2017; Nevison 2016; White 2016; Baisden and others 2018). This is particularly true for cultivars, which are narrowly defined in this study. White (2016) also demonstrated that as cultivars become increasingly altered, however, they are less likely to provide equivalent ecosystem services. More research on this topic is needed, but the species representation metric could approximate the diversity of ecosystem services provided by ETF natives in the mid-Atlantic horticulture trade.
Even though ETF natives represented a sizeable minority of the total species represented, gardeners have indicated that the biggest impediments to purchasing native plants are a lack of availability at retail centers, low species diversity, and insufficient quantities (Brzuszek and others 2010). This research was performed several years ago in the southeastern US, but similar complaints are frequently made in the mid-Atlantic region today. It has been demonstrated that client request is the main reason nurseries choose to sell native plants (for example, Brzuszek and Harkess 2009). Those wishing to purchase native plants wield considerable influence. Any efforts to increase native plant availability should encourage consumers to request natives wherever they shop for plants.
Invasive Plants
Out of 6885 different taxa grown by regional nurseries, only 4% were considered invasive in New York, Pennsylvania, New Jersey, Delaware, Maryland, and Virginia (see Table 2). This finding does not account for sales quantities, so while the taxa may be few, their proportion of sales could be markedly different. Also, one species, Miscanthus sinensis Andersson (Poaceae), accounted for 67 out the total 305 invasive taxa. Those numbers included cultivars as they are most often just as invasive as the species. Cultivars of invasive species that are not believed to be invasive, like those bred for sterility, were not categorized as invasive in this study. In terms of species representation, 46 invasive species were represented in our survey (see Table 2). The species in this survey that are considered invasive in mid-Atlantic states are listed in Table 3.
CONCLUSIONS
Although this survey did not account for sales quantities, the diversity metrics provide a valuable snapshot of the mid-Atlantic horticulture industry. Such data can be used by native plant advocates, such as the Mt. Cuba Center, to guide programming decisions that are most likely to increase native plant usage among horticulture professionals and the gardening public. Results are also beneficial to trade organizations and government agencies that wish to develop effective strategies for mitigating the risks posed by invasive plants used for horticultural purposes. We recommend that this study serve as a baseline for future surveys to evaluate long-term changes in horticultural plant diversity in the mid-Atlantic region.
Footnotes
Photos courtesy of Mt. Cuba Center