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1

Pearse, Ian S., and Andrew L. Hipp. "Native plant diversity increases herbivory to non-natives." Proceedings of the Royal Society B: Biological Sciences 281, no. 1794 (2014): 20141841. http://dx.doi.org/10.1098/rspb.2014.1841.

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There is often an inverse relationship between the diversity of a plant community and the invasibility of that community by non-native plants. Native herbivores that colonize novel plants may contribute to diversity–invasibility relationships by limiting the relative success of non-native plants. Here, we show that, in large collections of non-native oak trees at sites across the USA, non-native oaks introduced to regions with greater oak species richness accumulated greater leaf damage than in regions with low oak richness. Underlying this trend was the ability of herbivores to exploit non-na
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2

Meyer, Mary H., and Helen C. Harrison. "Using Native Plants." HortScience 32, no. 3 (1997): 493A—493. http://dx.doi.org/10.21273/hortsci.32.3.493a.

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Using Native Plants is a 120-min videotape that was developed as a result of a Cooperative Extension Partnership Programming Grant between the Univ. of Minnesota, Minnesota Extension Service and the Cooperative Extension–Univ. of Wisconsin-Extension. The content covers woodland wildflowers, prairie establishment and maintenance, landscaping lakeshores, and using native plants in traditional gardens settings.Video segments include: Eloise Butler Wildflower garden, Minneapolis, Minn.; Curtis Prairie, Madison, Wis.; Big Sandy Lake, Minn.; and the Minnesota Landscape Arboretum, Chanhassen. Develop
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3

Yessoufou, Kowiyou. "The Patterns of Intraspecific Variations in Mass of Nectar Sugar along a Phylogeny Distinguish Native from Non-Native Plants in Urban Greenspaces in Southern England." Plants 12, no. 18 (2023): 3270. http://dx.doi.org/10.3390/plants12183270.

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To serve human needs, non-native species are selected based on an array of functional traits, which generally confer competitive advantages to these species in their recipient environments. Identifying non-obvious functional traits that indirectly inform human selection of non-natives to introduce into urban greenspaces is not yet part of common discussions in invasion biology. We tested whether functional traits integrated within a phylogenetic framework, may reveal those subtle criteria underlying the introduction of non-native plants into urban greenspaces. We found no differences in terms
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4

Aslan, Clare, and Marcel Rejmanek. "Native fruit traits may mediate dispersal competition between native and non-native plants." NeoBiota 12 (February 15, 2012): 1–24. https://doi.org/10.3897/neobiota.12.2357.

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Seed disperser preferences may mediate the impact of invasive, non-native plant species on their new ecological communities. Significant seed disperser preference for invasives over native species could facilitate the spread of the invasives while impeding native plant dispersal. Such competition for dispersers could negatively impact the fitness of some native plants. Here, we review published literature to identify circumstances under which preference for non-native fruits occurs. The importance of fruit attraction is underscored by several studies demonstrating that invasive, fleshy-fruited
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5

Thynne, Jenny. "Observations of native bees and native plants." Metamorphosis Australia : magazine of the Butterfly & Other Invertebrates Club 102 (December 2021): 12–18. https://doi.org/10.5962/p.420272.

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6

Ornduff, Robert. "Native Plants: Conservation Priorities." Science 243, no. 4898 (1989): 1535. http://dx.doi.org/10.1126/science.243.4898.1535.b.

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7

ORNDUFF, R. "Native Plants: Conservation Priorities." Science 243, no. 4898 (1989): 1535. http://dx.doi.org/10.1126/science.243.4898.1535-a.

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8

Flint, Harrison L. "Native Plants: Another View." Arnoldia 58, no. 3 (1998): 30–32. http://dx.doi.org/10.5962/p.251208.

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9

Sun, Yan, and Aline Junod. "Invasive plants differ from native plants in their impact on native communities." Journal of Vegetation Science 28, no. 6 (2017): 1250–59. http://dx.doi.org/10.1111/jvs.12582.

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10

Liu, X. A., Y. Peng, J. J. Li, and P. H. Peng. "Enhanced shoot investment makes invasive plants exhibit growth advantages in high nitrogen conditions." Brazilian Journal of Biology 79, no. 1 (2019): 15–21. http://dx.doi.org/10.1590/1519-6984.169578.

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Abstract Resource amendments commonly promote plant invasions, raising concerns over the potential consequences of nitrogen (N) deposition; however, it is unclear whether invaders will benefit from N deposition more than natives. Growth is among the most fundamental inherent traits of plants and thus good invaders may have superior growth advantages in response to resource amendments. We compared the growth and allocation between invasive and native plants in different N regimes including controls (ambient N concentrations). We found that invasive plants always grew much larger than native pla
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11

Staab, Michael, Maria Helena Pereira-Peixoto, and Alexandra-Maria Klein. "Exotic garden plants partly substitute for native plants as resources for pollinators when native plants become seasonally scarce." Oecologia 194, no. 3 (2020): 465–80. http://dx.doi.org/10.1007/s00442-020-04785-8.

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Abstract Urban green spaces such as gardens often consist of native and exotic plant species, which provide pollen and nectar for flower-visiting insects. Although some exotic plants are readily visited by pollinators, it is unknown if and at which time of the season exotic garden plants may supplement or substitute for flower resources provided by native plants. To investigate if seasonal changes in flower availability from native vs. exotic plants affect flower visits, diversity and particularly plant–pollinator interaction networks, we studied flower-visiting insects over a whole growing se
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12

Alvarez, Erin, Sloane M. Scheiber, and David R. Sandrock. "Irrigation Requirements and Drought Response of Two Ornamental Grass Species." HortScience 41, no. 4 (2006): 1009B—1009. http://dx.doi.org/10.21273/hortsci.41.4.1009b.

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Water use is the most important environmental issue facing the horticulture industry. As a result, many water management districts are recommending native plants for their putative low-water requirements. Numerous textbooks and trade journals claim native plants use less water than non-natives; however, previous research found no difference in water use efficiency in the field between native and non-native species. Furthermore, recommendations of ornamental grasses for use as low-maintenance and low-water-requiring landscape plants have recently escalated. This study evaluated non-native Misca
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13

Wijesundara, D. S. A. "Can native plants become invasive?" Ceylon Journal of Science 46, no. 1 (2017): 1. http://dx.doi.org/10.4038/cjs.v46i1.7412.

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14

Payne, Jerry A. "IN DEFENSE OF NATIVE PLANTS." HortScience 25, no. 10 (1990): 1202a—1202. http://dx.doi.org/10.21273/hortsci.25.10.1202a.

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15

Koester, Heiko. "Native plants and urban sustainability." Native Plants Journal 9, no. 3 (2008): 323–33. http://dx.doi.org/10.2979/npj.2008.9.3.323.

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16

Roberts, L. "Extinction Imminent for Native Plants." Science 242, no. 4885 (1988): 1508. http://dx.doi.org/10.1126/science.242.4885.1508.

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17

Pearse, Ian, and Florian Altermatt. "Introduced Plants and Native Herbivores." Bulletin of the Ecological Society of America 96, no. 4 (2015): 629–34. http://dx.doi.org/10.1890/0012-9623-96.4.629.

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18

Mastnak, Tomaz, Julia Elyachar, and Tom Boellstorff. "Botanical Decolonization: Rethinking Native Plants." Environment and Planning D: Society and Space 32, no. 2 (2014): 363–80. http://dx.doi.org/10.1068/d13006p.

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19

Uekötter, Frank. "Native plants: A Nazi obsession?" Landscape Research 32, no. 3 (2007): 379–83. http://dx.doi.org/10.1080/01426390701318338.

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20

Paschke, Mark W. "Roadside Use of Native Plants." Restoration Ecology 10, no. 1 (2002): 171. http://dx.doi.org/10.1046/j.1526-100x.2002.10119.x.

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21

Storer, Susan. "Cultivating Native Plants: The Possibilities." Arnoldia 47, no. 2 (1987): 16–19. http://dx.doi.org/10.5962/p.258404.

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22

Huang, H. "Conserving Native Plants in China." Science 297, no. 5583 (2002): 935b—936. http://dx.doi.org/10.1126/science.297.5583.935b.

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23

Karim, M. N., and Azim U. Mallik. "Roadside revegetation by native plants." Ecological Engineering 32, no. 3 (2008): 222–37. http://dx.doi.org/10.1016/j.ecoleng.2007.11.003.

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24

Jose, Shibu. "Managing native and non-native plants in agroforestry systems." Agroforestry Systems 83, no. 2 (2011): 101–5. http://dx.doi.org/10.1007/s10457-011-9440-1.

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25

Aslan, Clare E., and Brett G. Dickson. "Non-native plants exert strong but under-studied influence on fire dynamics." NeoBiota 61 (October 8, 2020): 47–64. http://dx.doi.org/10.3897/neobiota.61.51141.

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Altered fire regimes are among the most destructive consequences of anthropogenic environmental change. Fires have increased in frequency in some regions, and invasion by fire-adapted non-native species has been identified as a major driver of this change, which results in a feedback cycle promoting further spread by the non-native species and diminishing occurrence of natives. We notice, however, that non-native species are often invoked in passing as a primary cause of changing fire dynamics, but that data supporting this claim are rarely presented. We therefore performed a meta-analysis of
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26

Aslan, Clare E., and Brett G. Dickson. "Non-native plants exert strong but under-studied influence on fire dynamics." NeoBiota 61 (October 8, 2020): 47–64. https://doi.org/10.3897/neobiota.61.51141.

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Altered fire regimes are among the most destructive consequences of anthropogenic environmental change. Fires have increased in frequency in some regions, and invasion by fire-adapted non-native species has been identified as a major driver of this change, which results in a feedback cycle promoting further spread by the non-native species and diminishing occurrence of natives. We notice, however, that non-native species are often invoked in passing as a primary cause of changing fire dynamics, but that data supporting this claim are rarely presented. We therefore performed a meta-analysis of
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27

Koziol, Liz, Thomas P. McKenna, and James D. Bever. "Native Microbes Amplify Native Seedling Establishment and Diversity While Inhibiting a Non-Native Grass." Plants 12, no. 5 (2023): 1184. http://dx.doi.org/10.3390/plants12051184.

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Although several studies have shown increased native plant establishment with native microbe soil amendments, few studies have investigated how microbes can alter seedling recruitment and establishment in the presence of a non-native competitor. In this study, the effect of microbial communities on seedling biomass and diversity was assessed by seeding pots with both native prairie seeds and a non-native grass that commonly invades US grassland restorations, Setaria faberi. Soil in the pots was inoculated with whole soil collections from ex-arable land, late successional arbuscular mycorrhizal
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28

YEK, Sze Huei, Zhi Hoong WONG, and Pei Wen HON. "Non-Native Plants Provide Nectar and Host Plant Resources to Native Butterflies." Journal of Tropical Biology & Conservation (JTBC) 21 (November 14, 2024): 88–95. http://dx.doi.org/10.51200/jtbc.v21i.5590.

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Urban restoration projects often aim to completely remove non-native plant species from the restored landscape and replace them with native plant species. However, this is unrealistic as early successional plants in urban settings comprise predominantly of non-native plant species. In this study, we investigate whether native butterfly species showed a preference on using native versus non-native plant species in their nectar sourcing and caterpillar host plant choice in two urban gardens at Monash University Malaysia. Native butterflies significantly preferred non-native plant species as nect
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29

Wari, David, Junichiro Abe, and Toshio Kitamura. "Native Japanese Polygonaceae Species as Potential Native Insectary Plants in Conserving Indigenous Natural Enemies." Insects 16, no. 2 (2025): 232. https://doi.org/10.3390/insects16020232.

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Conservation biological control (CBC) is the application of agricultural practices that utilize insectary plants to conserve and enhance natural enemies, thereby increasing their efficiency to suppress pests. Most of the insectary plants used in CBC are non-native invasive insectary plants, which are costly and pose threats to the local ecosystems and biodiversity. Alternative to non-native insectary plants, the use of native plants is proposed. Hence, the aim of this study is to identify native plant species that can be used as alternatives to non-native insectary plants to conserve and promo
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30

Potter, Daniel A., and Bernadette M. Mach. "Non-Native Non-Apis Bees Are More Abundant on Non-Native Versus Native Flowering Woody Landscape Plants." Insects 13, no. 3 (2022): 238. http://dx.doi.org/10.3390/insects13030238.

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Urban ecosystems can support diverse communities of wild native bees. Because bloom times are conserved by geographic origin, incorporating some non-invasive non-native plants in urban landscapes can extend the flowering season and help support bees and other pollinators during periods when floral resources from native plants are limiting. A caveat, though, is the possibility that non-native plants might disproportionately host non-native, potentially invasive bee species. We tested that hypothesis by identifying all non-native bees among 11,275 total bees previously collected from 45 species
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31

Garcillán, Pedro P., and Carlos Martorell. "Time since first record and population density influence range sizes of non-native plants, but also of native plants, in a chronically overgrazed island." Plant Ecology and Evolution 154, no. 2 (2021): 173–82. http://dx.doi.org/10.5091/plecevo.2021.1806.

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Background and aims − Humans are increasingly introducing species to new regions. It is necessary to understand the processes that drive the expansion of non-native species into these new habitats across multiple spatiotemporal scales.Material and methods − We studied the spatial distribution of the non-native flora (39 species) of Guadalupe Island (246 km2) in the Mexican Pacific. We analyzed how residence time (time since first report in historical sources, 1875–2004) and species attributes (population density, flowering phenology, and individual height) are related with range sizes of non-n
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32

Hu, Yi-Heng, Yu-Lu Zhou, Jun-Qin Gao, Xiao-Ya Zhang, Ming-Hua Song, and Xing-Liang Xu. "Plasticity of Plant N Uptake in Two Native Species in Response to Invasive Species." Forests 10, no. 12 (2019): 1075. http://dx.doi.org/10.3390/f10121075.

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Survival competition caused by limiting nutrients is often strong between invasive and native plant species. The effects of plant invasion on nutrient uptake in plant growth remain largely unclear. Clarifying how invasive plants affect N uptake by natives will provide a better understanding on mechanisms responsible for plant invasion. A 15N-labeling experiment was conducted using two common invasive species (Alternanthera philoxeroides (Mart.) Griseb. and Wedelia trilobata (L.) Hitchc.) and their native congeners (A. sessilis (L.) DC. and W. chinensis (Osbeck.) Merr.) to examine their growth
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33

Aslan, Clare, and Marcel Rejmanek. "Native fruit traits may mediate dispersal competition between native and non-native plants." NeoBiota 12 (February 15, 2012): 1–24. http://dx.doi.org/10.3897/neobiota.12.2357.

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34

Malenica, Frane, and Lucija Žinić. "Garden plants and butter knives." Jezikoslovlje 20, no. 3 (2019): 497–530. http://dx.doi.org/10.29162/jez.2019.18.

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Compounds are a frequent occurrence in the English language, but the way in which speakers, both native and non-native, process compounds is still a topic of discussion. Two factors have an influence on the recog-nition speed of compounds – lexical priming and relation priming. The former refers to faster recognition if a target and a prime compound share a common lexeme, while the latter refers to the inner relationships be-tween modifiers and heads within a compound. The study conducted by Gagné & Spalding (2004) shows a significant effect of relation priming on recognition of famili
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35

ASLAN, CLARE E., ERIKA S. ZAVALETA, DON CROLL, and BERNIE TERSHY. "Effects of Native and Non-Native Vertebrate Mutualists on Plants." Conservation Biology 26, no. 5 (2012): 778–89. http://dx.doi.org/10.1111/j.1523-1739.2012.01885.x.

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36

Garcillán, Pedro, and Carlos Martorell. "Time since first record and population density influence range sizes of non-native plants, but also of native plants, in a chronically overgrazed island." Plant Ecology and Evolution 154, no. (2) (2021): 173–82. https://doi.org/10.5091/plecevo.2021.1806.

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<b>Background and aims</b> − Humans are increasingly introducing species to new regions. It is necessary to understand the processes that drive the expansion of non-native species into these new habitats across multiple spatiotemporal scales.<b>Material and methods</b> − We studied the spatial distribution of the non-native flora (39 species) of Guadalupe Island (246 km2) in the Mexican Pacific. We analyzed how residence time (time since first report in historical sources, 1875–2004) and species attributes (population density, flowering phenology, and individual height) are related with range
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37

Torres, Ariana P., Alicia L. Rihn, Susan S. Barton, and Bridget K. Behe. "Perceptions and Socioeconomic Status Influence Purchases of Native Plants." HortTechnology 34, no. 2 (2024): 153–60. http://dx.doi.org/10.21273/horttech05345-23.

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Plants native to the United States, defined as those being present before European settlement, have aesthetic and environmental benefits. In 2018, only 10% of plant sales were native plants, a plant category that tends to be underrepresented in many residential and commercial landscapes. Although earlier research indicated that consumers find native plants less aesthetically appealing relative to introduced species, more recent research reported a growing demand for native plants. Thus, a better understanding of consumer perceptions would facilitate their marketing. We used an online survey of
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38

Hingston, Andrew B. "Does the introduced bumblebee, Bombus terrestris (Apidae), prefer flowers of introduced or native plants in Australia?" Australian Journal of Zoology 53, no. 1 (2005): 29. http://dx.doi.org/10.1071/zo04048.

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Proponents of importation of the European bumblebee, Bombus terrestris (L.), into Australia for pollination of commercial greenhouse crops argue that this species will have little impact on Australian native ecosystems because it prefers to forage on flowers of introduced species of plants rather than Australian native plants. However, data presented as evidence of preference for introduced plants have been equivocal. This study compared the attractiveness of introduced and Australian native plants to free-foraging B. terrestris in a garden at the interface between an urban area and native veg
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Mulder, Christa P. H., and Katie V. Spellman. "Do longer growing seasons give introduced plants an advantage over native plants in Interior Alaska?" Botany 97, no. 6 (2019): 347–62. http://dx.doi.org/10.1139/cjb-2018-0209.

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In interior Alaska, increases in growing season length and rapid expansion of introduced species are altering the environment for native plants. We evaluated whether earlier springs, warmer summers, and extended autumns alter the phenology of leaves and flowers in native and introduced forbs and shrubs in the boreal understory and open-canopy habitats, and whether the responses provide an advantage to either group. We tracked the phenology of 29 native and 12 introduced species over three years with very different spring, summer, and autumn conditions. The native species produced flowers (but
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40

Hopkins, E., and R. Al-Yahyai. "LANDSCAPING WITH NATIVE PLANTS IN OMAN." Acta Horticulturae, no. 1097 (September 2015): 181–92. http://dx.doi.org/10.17660/actahortic.2015.1097.22.

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41

Gikaara, D. M., M. E. Johnston, and D. G. Edwards. "PHOSPHORUS MANAGEMENT OF AUSTRALIAN NATIVE PLANTS." Acta Horticulturae, no. 683 (June 2005): 133–40. http://dx.doi.org/10.17660/actahortic.2005.683.13.

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42

Freeman, Susanne. "Contact dermatitis to Australian native plants." Medical Journal of Australia 145, no. 6 (1986): 302–3. http://dx.doi.org/10.5694/j.1326-5377.1986.tb101142.x.

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43

Lamont, G. P. "AUSTRALIAN NATIVE PLANTS AS CUT FLOWERS." Acta Horticulturae, no. 205 (March 1987): 83–88. http://dx.doi.org/10.17660/actahortic.1987.205.13.

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44

Gettys, Lyn A., and Kimberly A. Moore. "Greenhouse Production of Native Aquatic Plants." HortTechnology 29, no. 1 (2019): 41–45. http://dx.doi.org/10.21273/horttech04212-18.

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Wetland restoration is critical for improving ecosystem services, but many aquatic plant nurseries do not have facilities like those typically used for large-scale plant production. We questioned if we could grow littoral aquatic plant species in a variety of substrates and irrigation methods similar to those used for traditional greenhouse production. Plants were grown in pots with drainage holes that were filled with potting substrate, topsoil, coarse builders’ sand, or a 50/50 mix of topsoil and builders’ sand. These substrates were amended with 2 g of 15N–3.9P–10K controlled-release fertil
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Jiménez-Alfaro, Borja, Stephanie Frischie, Juliane Stolz, and Cándido Gálvez-Ramírez. "Native plants for greening Mediterranean agroecosystems." Nature Plants 6, no. 3 (2020): 209–14. http://dx.doi.org/10.1038/s41477-020-0617-3.

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46

McMahan, Linda R. "Cultivating Native Plants: The Legal Pitfalls." Arnoldia 47, no. 2 (1987): 20–24. http://dx.doi.org/10.5962/p.258403.

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47

Harper-Lore, Bonnie L. "Using native plants as problem-solvers." Environmental Management 20, no. 6 (1996): 827–30. http://dx.doi.org/10.1007/bf01205962.

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48

Sunny, Anupam, Swati Diwakar, and Gyan Prakash Sharma. "Native insects and invasive plants encounters." Arthropod-Plant Interactions 9, no. 4 (2015): 323–31. http://dx.doi.org/10.1007/s11829-015-9384-x.

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49

Brooker, Stanley G., Richard C. Cambie, and Robert C. Cooper. "Economic native plants of New Zealand." Economic Botany 43, no. 1 (1989): 79–106. http://dx.doi.org/10.1007/bf02859329.

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50

Messing, Russell H., Michelle N. Tremblay, Edward B. Mondor, Robert G. Foottit, and Keith S. Pike. "Invasive aphids attack native Hawaiian plants." Biological Invasions 9, no. 5 (2006): 601–7. http://dx.doi.org/10.1007/s10530-006-9045-1.

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