Next Article in Journal
Comprehensive Modulation of Secondary Metabolites in Terpenoid-Accumulating Mentha spicata L. via UV Radiation
Previous Article in Journal
The Influence of Climate Change on the Distribution of Hibiscus mutabilis in China: MaxEnt Model-Based Prediction
Previous Article in Special Issue
Anthriscus sylvestris—Noxious Weed or Sustainable Source of Bioactive Lignans?
 
 
Search for Articles:
Title / Keyword
Author / Affiliation / Email
Journal
Article Type
 
 
Advanced Search
 
Section
Special Issue
Volume
Issue
Number
Page
 
Journals
Plants
Volume 13
Issue 13
10.3390/plants13131745
plants-logo
Submit to this Journal Review for this Journal Propose a Special Issue
► Article Menu

Article Menu

share Share announcement Help format_quote Cite question_answer Discuss in SciProfiles thumb_up
...
Endorse textsms
...
Comment
first_page
settings
Order Article Reprints
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Review

The Invasive Alien Plant Solidago canadensis: Phytochemical Composition, Ecosystem Service Potential, and Application in Bioeconomy

by
Danijela Poljuha
1,*,†,
Barbara Sladonja
1,†,
Mirela Uzelac Božac
1,
Ivana Šola
2,
Danijela Damijanić
1 and
Tim Weber
3
1
Institute of Agriculture and Tourism, Karla Huguesa 8, 52440 Poreč, Croatia
2
Department of Biology, Faculty of Science, University of Zagreb, 10000 Zagreb, Croatia
3
Department of Molecular Life Sciences, University of Zurich, Winterthurerstrasse 190, CH-8057 Zurich, Switzerland
*
Author to whom correspondence should be addressed.
†
These authors contributed equally to this work.
Plants 2024, 13(13), 1745; https://doi.org/10.3390/plants13131745
Submission received: 18 April 2024 / Revised: 10 June 2024 / Accepted: 20 June 2024 / Published: 24 June 2024
(This article belongs to the Special Issue Invasive Alien Plant Species: From Phytochemical Diversity to Ecological Management)
Browse Figures
Versions Notes

Abstract

:
Solidago canadensis L. (Canadian goldenrod) is a widely distributed invasive herb from the Asteraceae family. It contains compounds that can change the soil structure and its nutritional components and thus affect indigenous species’ growth, germination, and survival. Consequently, it can pose a major ecological threat to biodiversity. On the other hand, many studies show that this species, due to its chemical properties, can be used for many positive purposes in pharmacy, agriculture, medicine, cosmetic industry, etc. S. canadensis contains a diverse array of bioactive compounds that may be responsible for antioxidant, antimicrobial, and anticancer activities. Many studies have discussed the invasiveness of S. canadensis, and several chemical and genetic differences between this plant in native and introduced environments have been discovered. Previous ecological and environmental evaluations of the potential of S. canadensis as an ecosystem services provider have come out with four promising groups of its products: active extracts, essential oil, fuel, and others. Although identified, there is a need for detailed validation and prioritisation of ecosystem services. This article aims to overview the S. canadensis invasive features, emphasising chemical characterisation and its potential for providing ecosystem services. Moreover, it identifies scenarios and proposes a methodology for estimating S. canadensis use in bioeconomy.

Graphical Abstract

1. Introduction

Invasive alien species (IAS) are not native to a particular ecosystem, and their introduction threatens ecosystems, habitats, or species [1]. By employing ‘competitive traits’, such as wide tolerance to environmental conditions, allelopathy, fast growth, and high fecundity, they permanently change the environment they inhabit [2,3,4], potentially reducing biodiversity and causing local species extinction. IAS can disrupt the delicate balance of ecosystems, leading to significant ecological and environmental changes. However, they can also provide numerous complex services to people [5].
Solidago canadensis L. (Canadian goldenrod) (Figure 1a) is an erect rhizomatous perennial plant native to North America [6]. It is one of 138 members of the Genus Solidago (Compositae, Asterales) [7], predominantly present in North America, with a few species also natively present in South America, Asia, and Europe.
The now-invasive S. canadensis was introduced to Europe in 1645 when it was planted in England as an ornamental plant [8]. The species thrives in forest edges, roadsides, and meadows [8,9] (Figure 1b) and is widespread (Figure 2). Since 2004, it has been listed on the EPPO (European and Mediterranean Plant Protection Organization) list of invasive alien plants [10].
For such plants, the EPPO recommends taking control measures and restrictions on sales and raising awareness due to the plant’s high potential to disrupt ecosystems and shift ecosystem services, which are already established [10]. Outside of Europe, China is also facing challenges with S. canadensis management, where it has completely dominated some areas and is now recognised as one of the most notorious species in the country [12].
Though each invasive alien plant species is unique, ecologists are trying to understand what common mechanisms govern their ability to dominate foreign environments. Canadian goldenrod appears to spread in an invasive manner [13] and could serve as a model invasive species. The case is particularly interesting because it challenges the view of the purely harmful invasive species and forces us to reconsider ecosystems as static networks. The Canadian goldenrod provides several benefits to its new habitats, as studied by Gallardo et al. [9], who looked at the impacts of this species in the French Alps. Authors [9] describe benefits in regulation, provisioning, and supporting ecosystem services by increasing pollinator presence, foraging, and storing carbon. Solidago flowers are protandrous and, as such, are an abundant source of nectar and pollen. The flowers thus increase nutrient availability for insects and often extend their foraging seasons [14]. These services are treasured by farmers and beekeepers in the region, observing increased yields in the area [9].
Canadian goldenrod also has noted ‘green synthesis’ capabilities, with noble metal nanoparticles [15,16] and biologically active compounds found in their tissues [17,18]. The plant itself can also be used for the production of natural dyes [19], cellulose [20], biopesticides [21], and as a pharmaceutical source [18,22]. On the other hand, the spread of the species in protected nature reserves threatens endemic and other endangered species [9].
Goldenrods are an example of a species requiring a thorough cost-benefit analysis for effective management. This analysis should consider both the benefits and potential threats of the plant in a specific habitat. Based on this assessment, appropriate actions can be taken to mitigate any negative impacts while maximizing benefits. The outcome brings about the best approximation of a species’ utility in a given area. It serves as a basis for a bioeconomic model that enables us to extract the added value of the plant while minimizing costs and the negative impact of the plant’s presence [23,24].
The present review aims to: (a) provide a general overview of species origin and distribution; (b) give a detailed review of its chemical composition; (c) explain the mechanisms of species invasiveness; (d) provide an overview of the S. canadensis ecosystem services; (e) identify scenarios for S. canadensis use in bioeconomy; and (f) identify gaps in current knowledge and give recommendations for future research.

2. Solidago canadensis Origin and Distribution

S. canadensis originated in North America [6], where it is cultivated as an ornamental plant, but is also widely spread as a weed [10]. Virtually ubiquitous in the USA and Canada, S. canadensis reaches as high as 65° N in the west of the continent [25,26]. It has been introduced in Europe, Siberia (western), Caucasus, Central Asia, the Himalayas, India, Indochina (Thailand), Malesia, China, Japan, and Australia [26]. According to the latest data, its distribution covers large areas of all continents except Africa and Antarctica (Figure 2) [11]. Apart from S. canadensis, there are a few invasive Solidago species originating from North America, with S. gigantea and S. altissima being the most prevalent. However, the taxonomic classification and nomenclature of the Solidago genus have undergone numerous changes, influenced by the evolving state of knowledge and varying approaches of different authors. Because of its native range in North America, S. canadensis is sometimes treated as an S. canadensis complex encompassing several different taxonomic units. The significant morphological variability of these taxa, the formation of hybrids, challenges in distinguishing them, and unresolved taxonomic status all contribute to the complexity of their classification and monitoring [11].
Even though S. canadensis is one of the most successful plant invaders [27], its further spread is still very likely because it is still available in the web catalogues of commercial nurseries.
Its dispersal happens in several ways: naturally by seeds and rhizomes, accidentally through human activities, and intentionally for its ornamental value [11]. Within its non-native habitat, S. canadensis is observed in various disturbed environments, predominantly along roadsides and railways, urban settings, abandoned fields, and grasslands [11]. It can also be found on the edges of forests, within open forests, along riverbanks, and in habitats disrupted or created by human activity. This species can occur in natural coastal communities, occasionally in semi-natural grassland and spring fen communities [8].

3. Phytochemical Composition of Solidago canadensis

In recent years, significant attention has been focused on the chemical composition of Solidago species, including S. canadensis, prompting intensive research efforts [28,29].
In the present review, publicly available literature references on the chemical profile of S. canadensis are studied, and sample type and origin, separation methods, and groups of identified compounds are summarised in Table 1.
Terpenoids constitute a broad and varied category of plant metabolites, encompassing mono-, sesqui-, and diterpenes. These aromatic volatile compounds contain different functional groups, such as alcohols, aldehydes, and ketones. Aromatic and medicinal plants produce secondary metabolites for defence against disease. For example, terpenoids, such as azadirachtin, carvone, menthol, ascaridole, methyl eugenol, toosendanin, and volkensin, have been shown to yield antimicrobial and antifungal properties, as well as insect pest repellent properties [42]. For example, Pandey et al. [42] showed that the oil from the medicinal plant Chenopodium ambrosioides has strong antibacterial activity against Erwinia herbicola and Pseudomonas putida that could be associated with the presence of α-terpinene, p-cymene, and ascaridole. Furthermore, Lippia alba essential oil was found to be an effective antifungal agent against Aspergillus flavus [43]. Due to their highly lipophilic nature and low molecular weight, terpenoids can disrupt the cell membrane, leading to cell death or inhibiting the sporulation and germination of fungi, on which the antimicrobial activity of essential oils is partly based [44]. Pyrethrins, a small class of specialized metabolites produced in Dalmatian pyrethrum (Tanacetum cinerariifolium) are active ingredients of the most widely used botanical insecticides against a wide range of pests [45]. Polyphenols, renowned bioactive compounds, are natural specialized metabolites that constitute an extensive collection of diverse chemicals found in plants, encompassing phytochemicals and enzymes. Moreover, since phenolics are primarily responsible for antioxidant properties and health benefits [46,47], which we pay the most attention to in this review, Table 2 summarises the most abundant individual phenolic compounds in different extracts of S. canadensis.
Extensive scientific research has been conducted on food sources abundant in these compounds, unveiling their potential health benefits [53,54,55,56]. Depending on the type of solvent, S. canadensis extract will have a different polyphenols profile [38,39,40]. In the study by Shelepova et al. [40], the proportions of identified polyphenols in extracts of inflorescences and leaves collected in Slovakia are revealed. Even though no statistical analyses are shown, it can be seen that in methanol, ethanol, and acetone extracts, the most predominant polyphenol is rutin (200.45 ± 5.95, 211.20 ± 6.50, and 211.14 ± 5.80 mg/g extract, respectively), while in the water extract, it is chlorogenic acid (834.50 ± 9.75 mg/g extract).
Hydroxycinnamic and hydroxybenzoic acids and flavonoids are the predominant polyphenols in S. canadensis herbs (Table 2). If we consider all bibliographic sources included in this paper and listed in Table 2, the total number of so far identified polyphenols is 39 (15 phenolic acids and 24 flavonoids). Among the phenolic acids, hydroxycinnamic acids are prevalent (11), while only four hydroxybenzoic acid compounds are present. In the group of flavonoids, flavonols are predominant (21 different structures), including quercetin and kaempferol and their derivatives.
Analysis of flavonoids in S. canadensis flowers revealed the presence of aglycones such as quercetin, kaempferol, and isorhamnetin, with quercetin being the most predominant [40]. Their glycoside forms were also recorded, and quercetin glycosides were dominantly represented both numerically and in concentration. The most noticeable difference between the flower and the leaf was the concentration of the glycosides rutin and hyperoside. Rutin was predominant in flowers and hyperoside was predominant in leaves [57]. Besides the mentioned flavonoids, chlorogenic and caffeic acid were also recorded in the entire aerial parts of S. canadensis plants collected in Hungary [38]. The study by Woźniak et al. [39] compared the aerial and underground parts of invasive populations of two equivalent Solidago species, S. canadensis L. and S. gigantea Aiton, in Poland. Quercetin and kaempferol and their glycosides dominated in aerial parts, followed by phenolic acids. The primary constituents in the underground parts identified in crude extracts and medium-polar fractions (ethanol, ethyl acetate, and butanol) were hydroxycinnamic-quinic acid conjugates. Notably, these conjugates predominantly consisted of isomers and derivatives of chlorogenic acid. However, hyperoside, a European Pharmacopoeia standard used for calculating flavonoid content in Solidaginis herba, was not recorded in these samples.
Depending on various factors, including ecological and climatic conditions, the ontogenesis phase, and the specific tissues of the plant, the quantity and chemical profile of essential oils (EOs) can vary significantly. The chemical compositions of EOs extracted from S. canadensis leaves, inflorescences, and roots collected in Hungary were compared [30]. The identified compounds were from the group of terpenoids. The EO yield was higher in leaves and inflorescences (0.20% and 0.18%, respectively) than in roots (0.04%). Inflorescences and roots had higher relative percentages of total identified terpenoids (94.3% and 96.2%, respectively) compared with leaves (85.5%), even though statistical analysis was not performed. Monoterpene hydrocarbons predominated based on mass in inflorescences and roots, while oxygenated sesquiterpenes were dominant in leaves. However, when we look at the percentages of the individual identified compounds, the most represented in each of the plant parts were monoterpenes; α-pinene was dominant in inflorescences (29.5 ± 4.5%), limonene in roots (32.7 ± 5.0%), and bornyl acetate in leaves (13.4 ± 2.8%). On the other hand, of the EOs in the green parts of S. canadensis collected in Poland, sesquiterpene germacrene D was the most abundant (23.8%) among the 16 annotated compounds. In this sample, two new sesquiterpenes were identified, the major 6-epi-β-cubebene and the minor 6-epi-α-cubebene [31]. Shelepova et al. [32] screened for the chemical composition of EOs in S. canadensis from ten different geographical areas in Eurasia, namely Austria, Ukraine, Kazakhstan, Russia (Moscow Main Botanical Garden, Krasnogorsk district, Penza, Tver, Sakhalin, Altaj and Tula regions). Of all the EOs, mono- and sesquiterpenes were dominant. Specifically, in the aerial parts of nine local S. canadensis populations, monoterpene α-pinene was predominant in five (from 24.3% in the Tula region to 52.4% in the Penza region), and bornyl acetate was predominant in one (26.3% in Tver’ region). Sesquiterpene germacrene D was the predominant EO in the other three populations (from 31.8% in Kazakhstan to 36.2% in the Sakhalin region). Plant material was collected at three different developmental stages in the Moscow Main Botanical Garden, and contributed to our understanding of how the chemical profiles of S. canadensis EOs evolve at different stages of the plant’s life cycle. The EO content varied from 0.1% in the leaves at the blooming stage, up to 0.70% in the leaves in the vegetative phase, both collected in Moscow Main Botanical Garden. In the blooming phase, inflorescences had more EOs (0.4%) than leaves (0.1%). Regarding the individual components, in the leaves at the vegetative stage, the predominant component was sesquiterpene germacrene D, with a proportion of 39.2%. In comparison, later in the blooming stage, monoterpene bornyl acetate dominated, with a proportion of 29.8%. In the inflorescences, however, the predominant EO was monoterpene α-pinene, with a proportion of 61.2%.
In the research by Amtmann et al. [41], the chemical compound contents in S. canadensis flower and honey were compared. GC-MS analyses revealed a higher number of individual aromatic compounds, mostly belonging to the classes terpenes and sesquiterpenes and their derivatives, in honey than in flowers. Germacrene-D was identified as a key compound in both the flowers and the resulting honey produced by bees that forage on S. canadensis nectar. Additional volatile compounds in honey were lactones, esters of open-chain acids, linoleic acid, and open-chain and ringed, saturated, and unsaturated hydrocarbons.

4. Behind the Invasiveness of S. canadensis

In recent years, significant scientific effort has been made to comprehend the mechanisms propelling the spread of invasive plants [58]. The success of many introduced species and the subsequent decline of native ones may be attributed to a combination of various factors [59]. Explaining these mechanisms will not only advance our understanding of plant competition and community ecology but also assist in managing introduced species, fostering conservation, and facilitating the restoration of native communities.
Many plant species are not dominant competitors in their native habitats, but once introduced into new ecosystems, they swiftly become invasive, outcompeting and displacing their new neighbours. A key hypothesis regarding the success of invasive plants suggests that they have evaded the co-evolved natural enemies that typically restrict them in their native regions [60]. Abhilasha et al. [61] conducted a study comparing the populations of S. canadensis under similar ecological conditions: in North America, where the species is indigenous, and in Switzerland, where it is invasive. Research showed that despite the lower herbivore pressure in Switzerland, S. canadensis had smaller inflorescences, fewer vegetative offspring, and lower growth compared to plants from the native North American range. This suggests that the successful invasion of this species must be based on other morphological traits, such as plant height and prolific production of seeds [62].
Plant population dynamics are strictly connected to climate change, and consequently, they also affect the distribution of invasive species [63]. Cao et al. [57] showed that S. canadensis exhibits more plasticity than some native species when it comes to reproductive phenology (prolonging the flowering duration and increasing reproductive investments and root/leaf ratio) in response to simulated climate change. In another research conducted by Bao et al. [64], the primary inquiry revolved around the impact of climate warming and increased precipitation on the growth and tolerance of S. canadensis during its establishment phase. In their conclusions, the authors suggested that the increased precipitation may fully counteract the inhibitory impacts of climate warming on the growth of S. canadensis, thereby maintaining its high resilience to heat stress. The impact of climate warming on the germination of S. canadensis was studied by [65]. The authors concluded that invasive populations of this species were more resistant to rising temperatures or climate change than native populations.
Another theory, also known as the novel weapon hypothesis, suggests that the primary factor driving the establishment and spread of invasive plants within undisturbed communities is the release of novel phytochemicals by the invader [66,67]. The invasive species produce allelopathic compounds with phytotoxic or at least fitness-reducing effects on plant neighbours that have not co-evolved [68]. Moreover, allelopathic effects of S. canadensis can be altered by the soil type, plant species identity, the origin of the Solidago plants, and the interacting effects of these factors. For example, S. canadensis samples from China had greater allelochemical contents than those from the native USA [69]. Recent S. canadensis metabolic analysis has revealed the existence of 122 metabolites, including flavonoids, phenylpropanoids, and terpenoids [70], which provide the plant allelopathic potential. Others found that S. canadensis affects the growth and seed germination of tested plants (Lactuca sativa, Morus alba, Pharbitis nil, Brassica campestris, Lepidium sativum, and others) [71,72,73]. The allelopathic effect was also observed in the research by Perera et al. [74] where S. canadensis leaf and flower extracts caused lower germination and seedling growth of different grassland plant species such as Festuca rubra L., Phleum pratense L., Poa pratensis L., Lotus corniculatus L., Trifolium repens L., and Silene flos-cuculi (L.) Greuter & Burdet.
The invasiveness of S. canadensis also lies in its ability to alter mineral soil nutrition [28]. Zhang et al. [75] reported that S. canadensis invasion decreased nitrate and phosphorus content and reduced soil stability. On the other hand, it increased soil organic carbon, ammonium, NH4, and pH. In addition, S. canadensis had higher nitrogen uptake capacity than native plants in China, such as Saccharum officinarum L., Lespedeza bicolor Turcz., and Sporobolus alterniflora Loisel [76]. Climate warming combined with nitrogen deposition significantly enhanced the growth performance of S. canadensis during the invasion process [77]. In agricultural soils, anthropogenic nitrogen input results in an elevated demand for phosphorus by plants. In such an environment, the competition among plant species may depend on their capacity to effectively utilize soil phosphorus sources [78]. In the case of S. canadensis, Wan et al. [78] detected a correlation between increased growth and elevated phosphorus, providing it with a competitive advantage over other plants. Similar findings were reported by Cui et al. [79], where high levels of phosphorus positively impacted the growth of S. canadensis. In addition to climate conditions, the nitrogen and phosphorus uptake may depend on the plant’s ploidy. Walczyk et al. [80] investigated diploid, autotetraploid, and autohexaploid varieties of S. gigantea, the close relative of S. canadensis. The results showed that diploids and polyploids invested more nitrogen and phosphorus into cells, and tetraploids grew more with nitrogen enrichments, suggesting that material costs increased with ploidy level. Within high-pH soils, the roots of S. canadensis secrete specialized metabolites that bind with biogenic metal ions and other cations, consequently diminishing nutrient accessibility to neighbouring plants [81,82]. The presence of S. canadensis increases the macronutrient cycle rate by boosting aboveground productivity and the accumulation of nutrients in plant biomass. Additionally, it leads to quicker nutrient release from litter and enhances soil microbial activity [83]. The inoculation of Arbuscular mycorrhizal fungi with S. canadensis increased the growth and its competitive ability to suppress neighbouring native plants [84]. The invasion success of S. canadensis may be attributed to its ability to maintain nutrient accumulation in shoots in response to competition with native plant communities [85]. Yang et al. [86] discovered that S. canadensis exhibited tolerance to heavy metal stress, while Bielecka et al. [87] found that this species could act as a phytostabilizer of Pb and Zn in heavily contaminated soils. S. canadensis also had a higher tolerance to Pb than native plants, which allowed this invasive species to suppress indigenous plant species and could encourage its rapid invasion in Pb-contaminated soil [75]. While various factors contribute to species’ invasiveness, overall, S. canadensis is a plant that outgrows native plants in nitrogen and phosphorus-rich soils, with the potential for phytoremediation of heavy metals.

5. Ecosystem Services

While changes to the structure and functioning of ecosystems induced by invasion are extensively documented [88], there is a limited understanding of the mechanisms connecting invasive alien species and ecosystem services [89]. The global focus on the repercussions of invasive species on ecosystem services has increased. Ecosystem services refer to natural ecosystems’ benefits to human society or, more broadly, the ecological processes that sustain human life. While the concept of ecosystem services is not new, numerous efforts have been made to quantify and classify these services, especially as new ones have been recognized [90]. Invasive alien species, including S. canadensis, can affect natural ecosystems, human habitats, and human well-being positively and negatively. These findings highlight the versatility of S. canadensis extracts, positioning them for use in medicine, agriculture, pharmaceutical, and textile industries [91].

5.1. Medicinal Ecosystem Services

For centuries, Solidago species have been used in European phytotherapy as herbal tea, tincture, or decoct for oral use, as antioxidant, anti-inflammatory, urological, and antiphlogistic remedies [38,92]. Today, the inflorescence of the Solidago species is authorized as a product for rheumatic and urinary complaints and for the prevention of cysto- and nephrolithiasis in several European countries [92]. S. canadensis is rich in specialized metabolite flavonoids (quercetin, kaempferol, and their glycosides, astragalin, and rutoside), anthocyanidins, triterpene saponins, phenolic acids (caffeic acid, chlorogenic acid, ferulic acid, synaptic, and vanillin acids), and essential oil (cadinene, α and β pinene, myrcene, limonene, sabinene, and germacren D) [92]. Due to their known radical scavenging ability, rutin, quercetin, and chlorogenic acid are particularly important in Solidago spp.
Extracts from aboveground S. canadensis parts, including stems, leaves, and inflorescences, demonstrate antibacterial activity against Listeria monocytogenes, Escherichia coli, Staphylococcus aureus, Salmonella sp., Staphylococcus faecalis, Bacillus subtilis, Klebsiella pneumoniae, and Pseudomonas aeruginosa [93,94]. This observation may contribute to the use of S. canadensis extracts as natural antimicrobials in dietary applications [79,80]. Deepa and Ravichandiran [95] found that various extracts of S. canadensis exhibited promising antibacterial activity against pathogenic bacteria like Salmonella typhi, surpassing the efficacy of ciprofloxacin, a commercial antibiotic, in in vitro disc diffusion assays. Additionally, Mishra et al. [96] investigated the properties of essential oils from Solidago canadensis roots using a method similar to the one by Deepa and Ravichandiran [95], revealing significant antibacterial activity against Streptococcus faecalis and Escherichia coli.
The research by Šutovská et al. [18] revealed that a polyphenolic–polysaccharide–protein complex isolated from S. canadensis could be used as an anti-asthmatic drug.
The essential oils (EOs) derived from various parts of S. canadensis, such as leaves, shoots, and roots, possess valuable features, including antifungal, antimutagenic, antibacterial, and antioxidant activities. These EOs can be used in dietary supplements, cosmetics, nutraceuticals, and pharmaceuticals [24]. The EOs’ chemical compositions include terpenes like germacrene-D, germacrene-A, a-humulene, b-caryophyllene, β-ylangene, 6-epi-α-cubebene, and 6-epi-β-cubebene, as well as α-pinene and limonene [31,36,97,98]. S. canadensis EOs also show significant antimicrobial activity, primarily due to their phenolic compounds, flavonoids, terpenoids, and polysaccharides [99].
Research also suggests anticancer potential in S. canadensis, with specific compounds, including labdane diterpene, showing cytotoxic activity against human lung cancer A549, colon cancer DLD-1, and normal fibroblasts WS1 cell lines [100].

5.2. Agriculture and Food Processing

Invasive plants may be important foraging resources for honeybees and wild pollinators [101]. As a late-season blooming plant, when many other plants have ceased flowering, S. canadensis is a valuable source of nectar for honeybees [102]. S. canadensis honey is considered a significant European unifloral honey mostly because of its unique sesquiterpene spectrum and aroma [35].
Preparations based on S. canadensis are also used in organic agriculture. This species’ essential oils (EOs) have demonstrated efficacy as botanical insecticides [41]. The EOs in S. canadensis, with components like α-pinene, germacrene, limonene, and β-pinene, demonstrate antifungal activity against Botrytis cinerea, a major contributor to the reduced post-harvest storage life of strawberries. Additionally, they demonstrate antifungal activity against both Monilinia fructicola and Penicillium expansum compared to Azoxystrobin, a fungicide with broad-spectrum efficacy [21,103]. Notably, the effect of EOs on B. cinerea aligned with the observations of [103], who found that the hyphae of B. cinerea underwent shrinkage and thinning after treatment with EOs. This mechanism corresponds to the proposed biological mechanism of EO action, leading to fungal cell wall damage and subsequent cell death. Additionally, EOs exhibit promising antibacterial activity against Pseudomonas fluorescens and Clavibacter michiganensis [21]. S. canadensis extracts also demonstrate effectiveness against harmful freshwater cyanobacteria, particularly Microcystis aeruginosa, presenting a potential application as an algaecide in small ponds [104]. Diterpenes, also common in Solidago, can act as insect antifeedants and growth inhibitors [105]. Given the acceptable ash content level, biochar derived from S. canadensis can be used in agriculture for enhancing soil water retention capacity, greenhouse cultivation, composting organic materials, and mitigating unpleasant odours [106]. As a result of torrefaction, one of the main steps when making biochar, the ash content in biochar from the S. canadensis increased to 20%.

5.3. Fuel

Biofuels, derived from processing biomass, present a viable alternative renewable energy source compared to fossil fuels [107]. Several articles have considered the use of S. canadensis as a methane fuel [108] and pellets [109]. Methane fuel has not shown much potential as a stand-alone product, but it can be combined with cattle slurry [108]. Ciesielczuk et al. [109] concluded that S. canadensis pellets could be considered great fuel due to their high calorific value (over 16 MJ kg−1), low moisture, low cost, and availability. Similar to those findings, Izydorczyk et al. [110] also confirmed 16.35 MJ/kg calorific value of goldenrod pellets, which is a slightly lower calorific value than the pellets available on the market. Considering the density of goldenrod growth and its calorific value, Ciesielczuk et al. [111] determined that a monoculture spanning one hectare could yield a calorific value of 288.4 GJ. In the research by Wiatrowska et al. [112], S. canadensis showed high ethanol efficiency after biomass conversion to bioethanol. S. canadensis biomass contains high lignin contents (28.68%), which leads to a high heating value of 19.894 MJ kg−1. Recent studies have shown that vegetative and generative parts of S. canadensis can be used as raw material in biochar production [106]. The observed results have shown a significant impact of the plant species and the sampled parts on the ash content, volatile matter content, calorific value, and heat of combustion. For biochar produced at a higher temperature, the calorific value and heat of combustion were both higher.

5.4. Others

Besides its application in the energy and agriculture sectors, S. canadensis biochar has the potential to be applied in environmental protection [113]. Recent studies indicate that biochar derived from a mixture of stems and leaves of S. canadensis has great potential for cadmium adsorption in water treatment. The highest achieved adsorption efficiency of Cd2+ was 95.6 ± 0.38% [114].
In the pulp and paper industry, there is an emphasis on replacing commercial fibres with sustainable alternatives. [20] reported using S. canadensis (SCL) stems to prepare a cellulose/SCL blend, which increased the stress value by about 7%, increased thermal stability by 75 °C, and reduced strain by about 35% compared to pure cellulose. In addition, S. canadensis extracts can be used as natural yellow dyes for textiles since they contain natural yellow dye compounds such as flavonoids quercetin, isoquercitrin, rutin, and kaempferol [19,115,116].
Moreover, this species contains flavonoids like aglycons, glycosides, and acetyl-glycosides, a wide range of polyphenolic compounds, saponins, hydroxycinnamates, and mineral elements, and it is assumed that they can reduce the metal ions to their nanoparticles [19]. Mariychuk et al. [15] reported the use of S. canadensis L. leaf extract for the eco-friendly synthesis of triangular and hexagonal gold nanoparticles. Similarly, Botha et al. [16] synthesized Silver (Ag), gold (Au), and Ag–Au bimetallic nanoparticles with the extracts of S. canadensis leaves.

6. Solidago canadensis as a Resource—Validating Scenarios in Bioeconomy

There have been several attempts to quantify the economic impact of invasive alien species (IAS) at different levels (species, nation, region). The global economic cost of IAS effects is tremendous, having at least quadrupled every decade since 1970 [117]. The impacts of IAS are typically assessed by evaluating environmental harm and financial repercussions. Many positive impacts of IAS on ecosystem services, which are difficult to measure in terms of money, are often disregarded [1]. The impacts of IAS on ecosystem services and sustaining its life support services can be incorporated by joining ecology and economics. Assessing potential solutions for the use of a singular invasive species is a significant challenge, involving the exploration of socio-economic benefits, enhanced added value, and the effective utilization of the species.
Bioeconomy, in a more specialized context, employs economic theories and techniques to enhance the effectiveness of management strategies concerning environmental matters [118]. As the ecosystem services framework of invasive species gains prominence in various aspects of environmental policy decision-making, there is a growing demand for valuation data to support these efforts, encompassing economic and non-economic factors [1].
Invasive species can be treated as local natural resources providing bioproducts with high added value. Bioeconomy has excellent potential and is vital for the sustainable use of resources and the preservation of ecosystems. It is a term that unites ecology, economics, policy, and management of invasive species [23].
When a species has multiple bioproducts, a methodology for evaluating the best ones can be helpful. It has been suggested that S. canadensis can provide multiple products as ecosystem services, and all parts of this plant can be used to obtain a useful product [24]. Here, we propose a methodology for the evaluation of S. canadensis use in bioeconomy (Figure 3). The same methodology can be applied to other invasive plant species or areas. Product evaluation is done considering both environmental and economic aspects.
The evaluation’s objective is to find out if there is a practical possibility of using S. canadensis for bioeconomy purposes by identifying the best scenarios with the most significant added value based on the complex data and processing. The best scenario is considered the one with the highest economic benefit and lowest negative impact on the environment or the highest positive impact. The proposed methodology starts with essential information gathering, followed by scenario choosing, socio-economic and environmental evaluation, and decision-making on use type prioritisation. Tested scenarios are extrapolated from the known groups of S. canadensis ecosystem services. Zihare and Blumberga [24] grouped all S. canadensis products into four groups: extracts, essential oils, fuel, and others. These can be detected as the most promising resources of S. canadensis, but inside the last group, “other”, a number of innovative resources can be identified. Further studies are necessary to test and score all feasible scenarios and consequently propose the most promising S. canadensis products.
New terms and concepts related to the bioeconomy have been coined in the last decade. While bioeconomy involves the logical and efficient utilization of bioresources, biotechonomy focuses on utilizing bioresources to create new value-added products that meet market demands and are competitive with existing products. Biotechonomy relies on advancing innovative biotechnologies to produce high-value products [119]. Another new concept linked to invasive species parts is the bioeconomic paradox described by Harris et al. [120]. It elaborates that reducing an invasive species’ population will reduce their catch rates and can make their use uneconomical. The authors investigated this seeming paradox through a bioeconomic case study involving the invasive lionfish (Pterois volitans).

7. Materials and Methods

The choice to focus specifically on Solidago canadensis, while setting aside other invasive species of the genus Solidago and their hybrids, is driven by our expertise and the prevalence of this species in our region. Our current scientific project investigates the phytochemistry, pharmaceutical potential, and possible new ecosystem services of various invasive species in Istria (Croatia), including S. canadensis.
The literature selection criteria for this review were based on the phytochemical composition underlying the mechanisms of S. canadensis invasiveness, as well as its potential to provide ecosystem services and its relevance to the bioeconomy. The literature search involved ScienceDirect, Web of Science, and Scopus databases, yielding an initial 2500–3500 entries related to the Solidago genus, with 600–900 references specifically pertaining to S. canadensis. The search was refined using the following keywords and their derivatives: origin, distribution, invasiveness, phytochemistry, chemical characterization, phenolics, bioactive compounds, ecosystem services, medicine, agriculture, fuel, soil, nanomaterials, energy, and bioeconomy. Three authors independently screened each report, each focusing on one of three areas: phytochemistry, ecosystem services, and bioeconomy. At least two authors reviewed the selection of each entry. Any questionable references and conclusions, as well as the overall approach and findings, were discussed collectively.

8. Conclusions

Solidago canadensis L. is a widely distributed invasive plant, whose presence and allelopathic properties can alter soil structure and nutrient composition, affecting the survival of native species, thus posing a significant ecological threat to biodiversity. In this paper, the mechanisms of its invasive properties and differences in native and introduction areas are explained. S. canadensis exhibits a wide variety of phytochemicals that play a significant role in both its invasiveness and its potential benefits. This comprehensive overview provides one of the first complete examinations of the chemical compounds present in this invasive species and explores its potential ecosystem services. Special emphasis is placed on its applications in medicine, agriculture, food, and biofuel production, as well as its application in the textile industry and nanotechnology development. The proposed methodology in bioeconomy can be used for prioritising and evaluating S. canadensis products as well as for any potential resource of invasive alien plants.

Author Contributions

Conceptualization, B.S. and D.P.; methodology, B.S. and I.Š.; validation, D.P. and B.S.; investigation, B.S., M.U.B., I.Š. and D.D.; data curation, M.U.B. and T.W.; writing—original draft preparation, D.P., B.S., M.U.B., I.Š., D.D. and T.W.; writing—review and editing, D.P., B.S., M.U.B., I.Š. and T.W.; visualization, D.P.; supervision, B.S.; project administration, D.P.; funding acquisition, D.P. All authors have read and agreed to the published version of the manuscript.

Funding

This research was supported by the Croatian Science Foundation under the project “NATURe as an ALLY: Alien Invasive Plants as Phytopharmaceuticals—NATURALLY” (IP-2020-02-6899). Mirela Uzelac Božac’s work was supported by the Croatian Science Foundation “Young Researchers’ Career Development Project–Training New Doctoral Students” (DOK-2021-02-3094).

Data Availability Statement

Not applicable.

Acknowledgments

We especially thank Kristina Grozić, the author of the Graphical Abstract, for her help and creativity.

Conflicts of Interest

The authors declare no conflict of interest. The funders had no role in the design of the study; in the collection, analyses, or interpretation of data; in the writing of the manuscript, or in the decision to publish the results.

References

  1. Pejchar, L.; Mooney, H.A. Invasive Species, Ecosystem Services and Human Well-Being. Trends Ecol. Evol. 2009, 24, 497–504. [Google Scholar] [CrossRef] [PubMed]
  2. Guido, A.; Pillar, V.D. Invasive Plant Removal: Assessing Community Impact and Recovery from Invasion. J. Appl. Ecol. 2017, 54, 1230–1237. [Google Scholar] [CrossRef]
  3. Keane, R.M.; Crawley, M.J. Exotic Plant Invasions and the Enemy Release Hypothesis. Trends Ecol. Evol. 2002, 17, 164–170. [Google Scholar] [CrossRef]
  4. Pyšek, P.; Richardson, D.M. Invasive Species, Environmental Change and Management, and Health. Annu. Rev. Environ. Resour. 2010, 35, 25–55. [Google Scholar] [CrossRef]
  5. Sladonja, B.; Poljuha, D.; Uzelac, M. Non-Native Invasive Species as Ecosystem Service Providers. In Ecosystem Services and Global Ecology; IntechOpen: Rijeka, Croatia, 2018. [Google Scholar] [CrossRef]
  6. Hegi, G. Illustrierte Flora von Mittel-Europa, Pteridophyta, Spermatophyta, Band III: Angiospermae, Dicotyledones 1, Teil 2, 1959–1979; Paul Parey: Berlin, Germany, 1979; ISBN 978-3-489-60020-6. [Google Scholar]
  7. Semple, J.C.; Beck, J.B. Revised Infrageneric Classification of Solidago (Asteraceae Astereae). Phytoneuron 2021, 10, 1–6. [Google Scholar]
  8. Kabuce, N.; Priede, N. NOBANIS—Invasive Alien Species Fact Sheet—Solidago canadensis. Available online: www.nobanis.org (accessed on 10 January 2024).
  9. Gallardo, B.; Bacher, S.; Bradley, B.; Comín, F.A.; Gallien, L.; Jeschke, J.M.; Sorte, C.J.B.; Vilà, M. InvasiBES: Understanding and Managing the Impacts of Invasive Alien Species on Biodiversity and Ecosystem Services. NeoBiota 2019, 50, 109–122. [Google Scholar] [CrossRef]
  10. EPPO Lists of Invasive Alien Plants. Available online: https://www.eppo.int/ACTIVITIES/invasive_alien_plants/iap_lists#iap (accessed on 12 January 2024).
  11. Popay, I.; Parker, C. Solidago canadensis (Canadian Goldenrod); CABI Compendium: Wallingford, UK, 2024. [Google Scholar] [CrossRef]
  12. Chen, G.; Zhang, C.; Ma, L.; Qiang, S.; Silander, J.A.; Qi, L.L. Biotic Homogenization Caused by the Invasion of Solidago canadensis in China. J. Integr. Agric. 2013, 12, 835–845. [Google Scholar] [CrossRef]
  13. Dong, M.; Lu, J.Z.; Zhang, W.J.; Chen, J.K.; Li, B. Canada Goldenrod (Solidago canadensis): An Invasive Alien Weed Rapidly Spreading in China. J. Syst. Evol. 2006, 44, 72–85. [Google Scholar] [CrossRef]
  14. Denisow, B.; Wrzesien, M. The Importance of Field-Margin Location for Maintenance of Food Niches for Pollinators. J. Apic. Sci. 2015, 59, 27–37. [Google Scholar] [CrossRef]
  15. Mariychuk, R.; Gruľová, D.; Grishchenko, L.; Linnik, R.; Lisnyak, V. Green Synthesis Of Non-Spherical Gold Nanoparticles Using Solidago canadensis L. Extract. Appl. Nanosci. 2020, 10, 4817–4826. [Google Scholar] [CrossRef]
  16. Botha, T.L.; Elemike, E.E.; Horn, S.; Onwudiwe, D.C.; Giesy, J.P.; Wepener, V. Cytotoxicity of Ag, Au and Ag-Au Bimetallic Nanoparticles Prepared Using Golden Rod (Solidago canadensis) Plant Extract. Sci. Rep. 2019, 9, 4169. [Google Scholar] [CrossRef] [PubMed]
  17. Shelepova, O.; Vinogradova, Y.; Vergun, O.; Grygorieva, O.; Brindza, J. Invasive Solidago canadensis L. as a Resource of Valuable Biological Compounds. Potravin. Slovak J. Food Sci. 2019, 13, 280–286. [Google Scholar] [CrossRef] [PubMed]
  18. Šutovská, M.; Capek, P.; Kocmálová, M.; Fraňová, S.; Pawlaczyk, I.; Gancarz, R. Characterization and Biological Activity of Solidago canadensis Complex. Int. J. Biol. Macromol. 2013, 52, 192–197. [Google Scholar] [CrossRef] [PubMed]
  19. Leitner, P.; Fitz-Binder, C.; Mahmud-Ali, A.; Bechtold, T. Production of a Concentrated Natural Dye from Canadian Goldenrod (Solidago canadensis) Extracts. Dyes Pigments 2012, 93, 1416–1421. [Google Scholar] [CrossRef]
  20. Ye, J.-R.; Wang, N.; Wang, H.; Luo, H.; Ren, Y.; Shen, Q. Structure and Properties of Cellulose/Solidago canadensis L. Blend. Cellul. Chem. Technol. 2015, 49, 275–280. [Google Scholar]
  21. Elshafie, H.S.; Gruľová, D.; Baranová, B.; Caputo, L.; De Martino, L.; Sedlák, V.; Camele, I.; De Feo, V. Antimicrobial Activity and Chemical Composition of Essential Oil Extracted from Solidago canadensis L. Growing Wild in Slovakia. Molecules 2019, 24, 1206. [Google Scholar] [CrossRef] [PubMed]
  22. Li, D.Q.; Pan, S.H.; Zhu, X.W.; Tan, L.; Cao, Y.F. Anticancer Activity and Chemical Composition of Leaf Essential Oil from Solidago canadensis L. in China. Adv. Mater. Res. 2011, 347–353, 1584–1589. [Google Scholar] [CrossRef]
  23. Pimentel, D. Bioeconomics of Invasive Species: Integrating Ecology, Economics, Policy, and Management. BioScience 2009, 59, 1002–1003. [Google Scholar] [CrossRef]
  24. Zihare, L.; Blumberga, D. Insight into Bioeconomy. Solidago canadensis as a Valid Resource. Brief Review. Energy Procedia 2017, 128, 275–280. [Google Scholar] [CrossRef]
  25. Weber, E. The Dynamics of Plant Invasions: A Case Study of Three Exotic Goldenrod Species (Solidago L.) in Europe. J. Biogeogr. 1998, 25, 147–154. [Google Scholar] [CrossRef]
  26. EPPO Global Database. Available online: https://gd.eppo.int/taxon/SOOCA/distribution/CA (accessed on 12 February 2024).
  27. Moroń, D.; Lenda, M.; Skórka, P.; Szentgyörgyi, H.; Settele, J.; Woyciechowski, M. Wild Pollinator Communities Are Negatively Affected by Invasion of Alien Goldenrods in Grassland Landscapes. Biol. Conserv. 2009, 142, 1322–1332. [Google Scholar] [CrossRef]
  28. Zhu, X.; Li, W.; Shao, H.; Tang, S. Selected Aspects of Invasive Solidago canadensis with an Emphasis on Its Allelopathic Abilities: A Review. Chem. Biodivers. 2022, 19, e202200728. [Google Scholar] [CrossRef] [PubMed]
  29. Fursenco, C.; Calalb, T.; Uncu, L.; Dinu, M.; Ancuceanu, R. Solidago virgaurea L.: A Review of Its Ethnomedicinal Uses, Phytochemistry, and Pharmacological Activities. Biomolecules 2020, 10, 1619. [Google Scholar] [CrossRef] [PubMed]
  30. Benelli, G.; Pavela, R.; Cianfaglione, K.; Nagy, D.U.; Canale, A.; Maggi, F. Evaluation of Two Invasive Plant Invaders in Europe (Solidago canadensis and Solidago gigantea) as Possible Sources of Botanical Insecticides. J. Pest Sci. 2019, 92, 805–821. [Google Scholar] [CrossRef]
  31. Kasali, A.A.; Ekundayo, O.; Paul, C.; König, W.A. Epi-Cubebanes from Solidago canadensis. Phytochemistry 2002, 59, 805–810. [Google Scholar] [CrossRef] [PubMed]
  32. Shelepova, O.; Vinogradova, Y.; Zaitchik, B.; Ruzhitsky, A.; Grygorieva, O.; Brindza, J. Constituents of the Essential Oil in Solidago canadensis L. from Eurasia. Potravin. Slovak J. Food Sci. 2018, 12, 20–25. [Google Scholar] [CrossRef] [PubMed]
  33. Xia, W.X.; He, W.; Wen, G.Y. The Constituents of the Essential Oil from Solidago canadensis L. Chin. Bull. Bot. 1999, 16, 178–181. [Google Scholar]
  34. Wang, K.J.; Li, N.; Chen, L.Z.; Yu, X.P. Chemical Constituents and Antifungal Activity of Essential Oil From Solidago canadensis. J. Plant Resour. Environ. 2006, 15, 34–36. [Google Scholar]
  35. Weyerstahl, P.; Marschall, H.; Christiansen, C.; Kalemba, D.; Góra, J. Constituents of the Essential Oil of Solidago canadensis (“Goldenrod”) from Poland—A Correction. Planta Med. 1993, 59, 281–282. [Google Scholar] [CrossRef] [PubMed]
  36. Kalemba, D.; Thiem, B. Constituents of the Essential Oils of Four Micropropagated Solidago Species. Flavour Fragr. J. 2004, 19, 40–43. [Google Scholar] [CrossRef]
  37. Nkuimi Wandjou, J.G.; Quassinti, L.; Gudžinskas, Z.; Nagy, D.U.; Cianfaglione, K.; Bramucci, M.; Maggi, F. Chemical Composition and Antiproliferative Effect of Essential Oils of Four Solidago Species (S. canadensis, S. gigantea, S. virgaurea and S.×niederederi). Chem. Biodivers. 2020, 17, e2000685. [Google Scholar] [CrossRef] [PubMed]
  38. Apati, P.; Szentmihályi, K.; Balázs, A.; Baumann, D.; Hamburger, M.; Kristó, T.S.; Szőke, É.; Kéry, Á. HPLC Analysis of the Flavonoids in Pharmaceutical Preparations from Canadian Goldenrod (Solidago canadensis). Chromatographia 2002, 56, S65–S68. [Google Scholar] [CrossRef]
  39. Woźniak, D.; Ślusarczyk, S.; Domaradzki, K.; Dryś, A.; Matkowski, A. Comparison of Polyphenol Profile and Antimutagenic and Antioxidant Activities in Two Species Used as Source of Solidaginis herba—Goldenrod. Chem. Biodiver. 2018, 15, e1800023. [Google Scholar] [CrossRef] [PubMed]
  40. Shelepova, O.; Vinogradova, Y.; Vergun, O.; Grygorieva, O.; Brindza, J. Assessment of Flavonoids and Phenolic Compound Accumulation in Invasive Solidago canadensis L. in Slovakia. Potravinarstvo Slovak. J. Food Sci. 2020, 14, 587–594. [Google Scholar] [CrossRef] [PubMed]
  41. Amtmann, M. The Chemical Relationship Between the Scent Features of Goldenrod (Solidago canadensis L.) Flower and Its Unifloral Honey. J. Food Compos. Anal. 2010, 23, 122–129. [Google Scholar] [CrossRef]
  42. Pandey, A.K.; Kumar, P.; Singh, P.; Tripathi, N.N.; Bajpai, V.K. Essential Oils: Sources of Antimicrobials and Food Preservatives. Front. Microbiol. 2017, 7, 2161. [Google Scholar] [CrossRef] [PubMed]
  43. Pandey, A.K.; Sonker, N.; Singh, P. Efficacy of Some Essential Oils Against Aspergillus flavus with Special Reference to Lippia alba Oil an Inhibitor of Fungal Proliferation and Aflatoxin B1 Production in Green Gram Seeds during Storage. J. Food Sci. 2016, 81, M928–M934. [Google Scholar] [CrossRef] [PubMed]
  44. Nazzaro, F.; Fratianni, F.; Coppola, R.; Feo, V. Essential Oils and Antifungal Activity. Pharmaceuticals 2017, 10, 86. [Google Scholar] [CrossRef] [PubMed]
  45. Lybrand, D.; Xu, H.; Last, R.; Pichersky, E. How Plants Synthesize Pyrethrins: Safe and Biodegradable Insecticides. Trends Plant Sci. 2020, 25, 1240–1251. [Google Scholar] [CrossRef] [PubMed]
  46. Kumar, N.; Goel, N. Phenolic acids: Natural Versatile Molecules With Promising Therapeutic Applications. Biotechnol. Rep. 2019, 24, e00370. [Google Scholar] [CrossRef] [PubMed]
  47. Singh, N.; Yadav, S.S. A Review On Health Benefits Of Phenolics Derived From Dietary Spices. Curr. Res. Food Sci. 2022, 5, 1508–1523. [Google Scholar] [CrossRef] [PubMed]
  48. Zekič, J.; Vovk, I.; Glavnik, V. Extraction and Analyses of Flavonoids and Phenolic Acids from Canadian Goldenrod and Giant Goldenrod. Forests 2021, 12, 40. [Google Scholar] [CrossRef]
  49. Papp, I.; Apáti, P.; Andrasek, V.; Blázovics, A.; Balázs, A.; Kursinszki, L.; Kite, G.C.; Houghton, P.J.; Kéryl, Á. LC/MS Analysis of Antioxidant Plant Phenoloids. Chromatographia 2004, 60, 93–100. [Google Scholar] [CrossRef]
  50. Kelly, A.M.; de Oliveira, T.B.; Valverde, S.S. Determination of the Metabolic Profile of Solidago canadensis Using UFLC-PDA-ESI-TOF. Rodriguesia 2020, 71, e01062019. [Google Scholar] [CrossRef]
  51. Abdel Baki, P.M.; El-Sherei, M.M.; Khaleel, A.E.; Abdel Motaal, A.A.; Ibrahim Abdallah, H.M. Aquaretic Activity of Solidago canadensis L. Cultivated in Egypt and Determination of the Most Bioactive Fraction. Iran. J. Pharm. Res. 2019, 18, 922–937. [Google Scholar] [CrossRef] [PubMed]
  52. Radušienė, J.; Karpavičienė, B.; Vilkickytė, G.; Marksa, M.; Raudonė, L. Comparative Analysis of Root Phenolic Profiles and Antioxidant Activity of Five Native and Invasive Solidago L. Species. Plants 2024, 13, 132. [Google Scholar] [CrossRef] [PubMed]
  53. Chu, A.J. Quarter-Century Explorations of Bioactive Polyphenols: Diverse Health Benefits. Front. Biosci. Landmark Ed. 2022, 27, 134. [Google Scholar] [CrossRef] [PubMed]
  54. Fraga, C.G.; Croft, K.D.; Kennedy, D.O.; Tomás-Barberán, F.A. The Effects of Polyphenols and Other Bioactives on Human Health. Food Funct. 2019, 10, 514–528. [Google Scholar] [CrossRef] [PubMed]
  55. Luca, S.V.; Macovei, I.; Bujor, A.; Miron, A.; Skalicka-Woźniak, K.; Aprotosoaie, A.C.; Trifan, A. Bioactivity of Dietary Polyphenols: The Role of Metabolites. Crit. Rev. Food Sci. Nutr. 2020, 60, 626–659. [Google Scholar] [CrossRef] [PubMed]
  56. Rana, A.; Samtiya, M.; Dhewa, T.; Mishra, V.; Aluko, R.E. Health Benefits of Polyphenols: A Concise Review. J. Food Biochem. 2022, 46, e14264. [Google Scholar] [CrossRef] [PubMed]
  57. Avertseva, I.N.; Suleymanova, F.S.; Nesterova, O.V.; Reshetnyak, V.Y.; Matveenko, V.N.; Zhukov, P.A. Study of Polyphenolic Compounds in Extracts from Flowers and Leaves of Canadian Goldenrod and Dwarf Goldenrod (Solidago canadensis L. and Solidago nana Nitt.). Mosc. Univ. Chem. Bull. 2020, 75, 47–51. [Google Scholar] [CrossRef]
  58. Catford, J.A.; Jansson, R.; Nilsson, C. Reducing Redundancy in Invasion Ecology by Integrating Hypotheses into a Single Theoretical Framework. Divers. Distrib. 2009, 15, 22–40. [Google Scholar] [CrossRef]
  59. Weiher, E. On the Status of Restoration Science: Obstacles and Opportunities. Restor. Ecol. 2007, 15, 340–343. [Google Scholar] [CrossRef]
  60. Vilà, M.; Weiner, J. Are Invasive Plant Species Better Competitors Than Native Plant Species?—Evidence from Pair-Wise Experiments. Oikos 2004, 105, 229–238. [Google Scholar] [CrossRef]
  61. Abhilasha, D.; Quintana, N.; Vivanco, J.; Joshi, J. Do Allelopathic Compounds in Invasive Solidago canadensis s.l. Restrain the Native European Flora? J. Ecol. 2008, 96, 993–1001. [Google Scholar] [CrossRef]
  62. Van Kleunen, M.; Schmid, B. No Evidence for an Evolutionary Increased Competitive Ability in an Invasive Plant. Ecology 2003, 84, 2816–2823. [Google Scholar] [CrossRef]
  63. Cao, Y.; Xiao, Y.; Zhang, S.; Hu, W. Simulated Warming Enhances Biological Invasion of Solidago canadensis and Bidens frondosa by Increasing Reproductive Investment and Altering Flowering Phenology Pattern. Sci. Rep. 2018, 8, 16073. [Google Scholar] [CrossRef] [PubMed]
  64. Bao, X.Y.; Wang, Z.X.; He, Z.S.; He, W.M. Enhanced Precipitation Offsets Climate Warming Inhibition on Solidago canadensis Growth and Sustains Its High Tolerance. Glob. Ecol. Conserv. 2022, 34, e02023. [Google Scholar] [CrossRef]
  65. Zhou, X.H.; He, W.M. Climate Warming Facilitates Seed Germination in Native but Not Invasive Solidago canadensis Populations. Front. Ecol. Evol. 2020, 8, 595214. [Google Scholar] [CrossRef]
  66. Cappuccino, N.; Arnason, J.T. Novel Chemistry of Invasive Exotic Plants. Biol. Lett. 2006, 2, 189–193. [Google Scholar] [CrossRef] [PubMed]
  67. Qu, T.; Du, X.; Peng, Y.; Guo, W.; Zhao, C.; Losapio, G. Invasive Species Allelopathy Decreases Plant Growth and Soil Microbial Activity. PLoS ONE 2021, 16, e0246685. [Google Scholar] [CrossRef] [PubMed]
  68. Callaway, R.M.; Aschehoug, E.T. Invasive Plants Versus Their New and Old Neighbors: A Mechanism for Exotic Invasion. Science 2000, 290, 521–523. [Google Scholar] [CrossRef] [PubMed]
  69. Yuan, Y.; Wang, B.; Zhang, S.; Tang, J.; Tu, C.; Hu, S.; Yong, J.W.H.; Chen, X. Enhanced Allelopathy and Competitive Ability of Invasive Plant Solidago canadensis In Its Introduced Range. J. Plant Ecol. 2013, 6, 253–263. [Google Scholar] [CrossRef]
  70. Likhanov, A.; Oliinyk, M.; Pashkevych, N.; Churilov, A.; Kozyr, M. The Role of Flavonoids in Invasion Strategy of Solidago canadensis L. Plants 2021, 10, 1748. [Google Scholar] [CrossRef] [PubMed]
  71. Wang, C.; Xiao, H.; Zhao, L.; Liu, J.; Wang, L.; Zhang, F.; Shi, Y.; Du, D. The Allelopathic Effects of Invasive Plant Solidago canadensis on Seed Germination and Growth of Lactuca sativa Enhanced by Different Types of Acid Deposition. Ecotoxicology 2016, 25, 555–562. [Google Scholar] [CrossRef] [PubMed]
  72. Yang, R.Y.; Mei, L.X.; Tang, J.J.; Chen, X. Allelopathic Effects of Invasive Solidago canadensis L. on Germination and Growth of Native Chinese Plant Species. Allelopathy J. 2007, 19, 241–248. [Google Scholar]
  73. Judžentienė, A.; Būdienė, J.; Labanauskas, L.; Stancelytė, D.; Nedveckytė, I. Allelopathic Activity of Canadian Goldenrod (Solidago canadensis L.) Extracts on Seed Germination and Growth of Lettuce (Lactuca sativa L.) and Garden Pepper Cress (Lepidium sativum L.). Plants 2023, 12, 1421. [Google Scholar] [CrossRef] [PubMed]
  74. Perera, P.C.D.; Chmielowiec, C.; Szymura, T.H.; Szymura, M. Effects Of Extracts From Various Parts Of Invasive Solidago species On the Germination and Growth of Native Grassland Plant Species. PeerJ 2023, 11, e15676. [Google Scholar] [CrossRef] [PubMed]
  75. Zhang, Q.; Tang, J.; Chen, X. Competitive Interaction Between the Invasive Solidago canadensis and Native Kummerowia striata in Lead Contaminated Soil. Bot. Stud. 2008, 49, 385–391. [Google Scholar]
  76. Wang, W.; Zhu, Q.; Dai, S.; Meng, L.; He, M.; Chen, S.; Zhao, C.; Dan, X.; Cai, Z.; Zhang, J.; et al. Effects of Solidago canadensis L. on Mineralization-Immobilization Turnover Enhance Its Nitrogen Competitiveness And Invasiveness. Sci. Total Environ. 2023, 882, 163641. [Google Scholar] [CrossRef] [PubMed]
  77. Ren, G.; Yang, B.; Cui, M.; Dai, Z.; Xiang, J.; Zhang, H.; Li, G.; Li, J.; Javed, Q.; Du, D. Warming And Elevated Nitrogen Deposition Accelerate The Invasion Process of Solidago canadensis L. Ecol. Process. 2022, 11, 62. [Google Scholar] [CrossRef]
  78. Wan, L.Y.; Qi, S.S.; Dai, Z.C.; Zou, C.B.; Song, Y.G.; Hu, Z.Y.; Zhu, B.; Du, D.L. Growth Responses Of Canada Goldenrod (Solidago canadensis L.) to Increased Nitrogen Supply Correlate With Bioavailability of Insoluble Phosphorus Source. Ecol. Res. 2018, 33, 261–269. [Google Scholar] [CrossRef]
  79. Cui, M.; Yang, B.; Ren, G.; Stevanato, P.; Fan, X.; Huang, P.; Sun, J.; Du, D. Increased and Fluctuating Phosphorus Nutrient Availability Positively Affects the Growth of the Invasive Plant Solidago canadensis. Flora 2023, 309, 152422. [Google Scholar] [CrossRef]
  80. Walczyk, A.M.; Hersch-Green, E.I. Genome-Material Costs and Functional Trade-Offs in the Autopolyploid Solidago gigantea (Giant Goldenrod) Series. Am. J. Bot. 2023, 110, e16218. [Google Scholar] [CrossRef] [PubMed]
  81. Ge, Y.; Wang, Q.; Wang, L.; Liu, W.; Liu, X.; Huang, Y.; Christie, P. Response of Soil Enzymes and Microbial Communities to Root Extracts of the Alien Alternanthera philoxeroides. Arch. Agron. Soil Sci. 2018, 64, 708–717. [Google Scholar] [CrossRef]
  82. Liao, M.; Xie, X.M.; Peng, Y.; Ma, A.L. Changes of Soil Microbiological Characteristics After Solidago canadensis L. Invasion. Agric. Sci. China 2011, 10, 1064–1071. [Google Scholar] [CrossRef]
  83. Ye, X.Q.; Yan, Y.N.; Wu, M.; Yu, F.H. High Capacity of Nutrient Accumulation by Invasive Solidago canadensis in a Coastal Grassland. Front. Plant Sci. 2019, 10, 575. [Google Scholar] [CrossRef] [PubMed]
  84. Dong, L.J.; Ma, L.N.; He, W.M. Arbuscular Mycorrhizal Fungi Help Explain Invasion Success of Solidago canadensis. Appl. Soil Ecol. 2020, 157, 103763. [Google Scholar] [CrossRef]
  85. Ye, X.Q.; Ma, R.X.; Lei, S.T.; Wu, M.; Yu, F.H. Maintained Nutrient Accumulation in Invasive Solidago canadensis in Response to Competition: Competition Tolerance And Nutrient Accumulation. Flora 2022, 295, 152136. [Google Scholar] [CrossRef]
  86. Yang, R.Y.; Tang, J.J.; Yang, Y.S.; Chen, X. Invasive and Non-Invasive Plants Differ in Response to Soil Heavy Metal Lead Contamination. Bot. Stud. 2007, 48, 453–458. [Google Scholar]
  87. Bielecka, A.; Królak, E. Solidago canadensis as a bioaccumulator and phytoremediator of Pb and Zn. Environ. Sci. Pollut. Res. 2019, 26, 36942–36951. [Google Scholar] [CrossRef] [PubMed]
  88. Mooney, H.A.; Hobbs, R.J. Invasive Species in a Changing World; Island Press: Washington, DC, USA, 2000. [Google Scholar]
  89. Charles, H.; Dukes, J.S. Impacts of Invasive Species on Ecosystem Services. In Biological Invasions; Nentwig, W., Ed.; Ecological Studies; Springer: Berlin/Heidelberg, Germany, 2007; pp. 217–237. [Google Scholar]
  90. National Research Council. Valuing Ecosystem Services: Toward Better Environmental Decision-Making; The National Academies Press: Washington, DC, USA, 2005. [CrossRef]
  91. Zihare, L.; Blumberga, D. Market Opportunities for Cellulose Products from Combined Renewable Resources. Environ. Clim. Technol. 2017, 19, 33–38. [Google Scholar] [CrossRef]
  92. European Medicines Agency, Committee on Herbal Medicinal Products (HMPC). Assessment Report For Herbal Substance(s), Herbal Preparations or Combinations Thereof With Traditional Use: Solidago virgaurea L., Herba. London, 4 September 2008. EMEA/HMPC/ 285759/2007. Available online: http://www.ema.europa.eu (accessed on 1 April 2024).
  93. Deng, Y.; Zhao, Y.; Padilla-Zakour, O.; Yang, G. Polyphenols, Antioxidant and Antimicrobial Activities of Leaf and Bark Extracts of Solidago canadensis L. Ind. Crops Prod. 2015, 74, 803–809. [Google Scholar] [CrossRef]
  94. Kołodziej, B.; Kowalski, R.; Kedzia, B. Antibacterial and Antimutagenic Activity of Extracts Aboveground Parts of Three Solidago Species: Solidago virgaurea L., Solidago canadensis L. and Solidago gigantea Ait. J. Med. Plant Res. 2011, 5, 6770–6779. [Google Scholar] [CrossRef]
  95. Deepa, N.; Ravichandiran, V. Antimicrobial Activity of Extractives of Solidago canadensis L. Int. J. Res. Pharm. Sci. 2010, 1, 411–413. [Google Scholar]
  96. Mishra, D.; Joshi, S.; Bisht, G.; Pilkhwal, S. Chemical Composition and Antimicrobial Activity of Solidago canadensis Linn. Root Essential Oil. J. Basic Clin. Pharm. 2010, 1, 187–190. [Google Scholar] [PubMed]
  97. Chanotiya, C.S.; Yadav, A. Natural Variability In Enantiomeric Composition of Bioactive Chiral Terpenoids in the Essential Oil of Solidago canadensis L. from Uttarakhand, India. Nat. Prod. Commun. 2008, 3, 263–266. [Google Scholar] [CrossRef]
  98. Prosser, I.; Altug, I.G.; Phillips, A.L.; Konig, W.A.; Bouwmeester, H.J.; Beale, M.H. Enantiospecific (+)- and (-)-Germacrene-D synthases, Cloned from Goldenrod, Reveal a Functionally Active Variant of the Universal Isoprenoid-biosynthesis Aspartate-Rich Motif. Arch. Biochem. Biophys. 2004, 432, 136–144. [Google Scholar] [CrossRef] [PubMed]
  99. Thiem, B.; Wesolowska, M.; Skrzypczak, L.; Budzianowski, J. Phenolic Compounds in Two Solidago, L. Species from In Vitro Culture. Acta Pol. Pharm. 2001, 58, 277–281. [Google Scholar] [PubMed]
  100. Bradette-Hébert, M.; Legault, J.; Lavoie, S.; Pichette, A. A New Labdane Diterpene from the Flowers of Solidago canadensis. Chem. Pharm. Bull. 2008, 56, 82–84. [Google Scholar] [CrossRef]
  101. Urbanowicz, C.; Muñiz, P.A.; McArt, S.H. Honey Bees and Wild Pollinators Differ in Their Preference for and Use of Introduced Floral Resources. Ecol. Evol. 2020, 10, 6741–6751. [Google Scholar] [CrossRef] [PubMed]
  102. Štefanić, E.; Puškadija, Z.; Štefanić, I.; Bubalo, D. Goldenrod: A Valuable Plant for Beekeeping in North-Eastern Croatia. Bee World 2003, 84, 88–92. [Google Scholar] [CrossRef]
  103. Liu, S.; Shao, X.; Wei, Y.; Li, Y.; Xu, F.; Wang, H. Solidago canadensis L. Essential Oil Vapor Effectively Inhibits Botrytis cinerea Growth and Preserves Post-Harvest Quality of Strawberry as a Food Model System. Front. Microbiol. 2016, 7, 1179. [Google Scholar] [CrossRef] [PubMed]
  104. Huang, Y.; Bai, Y.; Wang, Y.; Kong, H. Allelopathic Effects of the Extracts from an Invasive Species Solidago canadensis L. on Microcystis aeruginosa. Lett. Appl. Microbiol. 2013, 57, 451–458. [Google Scholar] [CrossRef] [PubMed]
  105. Weber, E. Biological Flora of Central Europe: Solidago altissima L. Flora 2000, 195, 123–134. [Google Scholar] [CrossRef]
  106. Łapczyńska-Kordon, B.; Ślipek, Z.; Słomka-Polonis, K.; Styks, J.; Hebda, T.; Francik, S. Physicochemical Properties of Biochar Produced from Goldenrod Plants. Materials 2022, 15, 2615. [Google Scholar] [CrossRef] [PubMed]
  107. Rodionova, M.; Poudyal, R.S.; Tiwari, I.; Voloshin, R.A.; Zharmukhamedov, S.K.; Nam, H.G.; Zayadan, B.K.; Bruce, B.D.; Hou, H.J.M.; Allakhverdiev, S.I. Biofuel Production: Challenges and Opportunities. Int. J. Hydrogen Energy 2017, 42, 8450–8461. [Google Scholar] [CrossRef]
  108. Yao, Y.; Sheng, H.; Luo, Y.; He, M.; Li, X.; Zhang, H.; He, W.; An, L. Optimization of Anaerobic Co-Digestion of Solidago canadensis L. Biomass and Cattle Slurry. Energy 2014, 78, 122–127. [Google Scholar] [CrossRef]
  109. Ciesielczuk, T.; Poluszyńska, J.; Rosik-Dulewska, C.; Sporek, M.; Lenkiewicz, M. Uses Of Weeds As An Economical Alternative To Processed Woodbiomass And Fossil Fuels. Ecol. Eng. 2016, 95, 485–491. [Google Scholar] [CrossRef]
  110. Izydorczyk, G.; Skrzypczak, D.; Kocek, D.; Mironiuk, M.; Witek-Krowiak, A.; Moustakas, K.; Chojnacka, K. Valorization of Bio-Based Post-Extraction Residues of Goldenrod and Alfalfa as Energy Pellets. Energy 2020, 194, 116898. [Google Scholar] [CrossRef]
  111. Ciesielczuk, T.; Poluszynska, J.; Sporek, M. Potential Uses For Solid Biofuels From NON-Food Crops. Proc. ECOpole 2014, 8, 23e6. [Google Scholar] [CrossRef]
  112. Wiatrowska, B.M.; Wawro, A.; Gieparda, W.; Waliszewska, B. Bioethanol Production Potential and Other Biomass Energy Properties of Invasive Reynoutria, Solidago,and Spiraea Plants. Forests 2022, 13, 1582. [Google Scholar] [CrossRef]
  113. Bartoli, M.; Giorcelli, M.; Jagdale, P.; Rovere, M.; Tagliaferro, A. A Review of Non-Soil Biochar Applications. Materials 2020, 13, 261. [Google Scholar] [CrossRef]
  114. Tang, J.W.; Cheng, J.H.; Wang, K.N.; Zhang, Q.Z. Characteristics and Mechanism of Cadmium Adsorption By Solidago canadensis-Derived Biochar. J. Agro-Environ. Sci. 2019, 38, 1339–1348. [Google Scholar]
  115. Bechtold, T.; Mahmud-Ali, A.; Mussak, R. Natural Dyes For Textile Dyeing: A Comparison Of Methods To Assess The Quality Of Canadian Golden Rod Plant Material. Dyes Pigm. 2007, 75, 287–293. [Google Scholar] [CrossRef]
  116. Mahmud-Ali, A.; Fitz-Binder, C.; Bechtold, T. Aluminium Based Dye Lakes From Plant Extracts For Textile Coloration. Dyes Pigm. 2012, 94, 533–540. [Google Scholar] [CrossRef]
  117. IPBES Summary for Policymakers of the Thematic Assessment Report on Invasive Alien Species and Their Control of the Intergovernmental Science-Policy Platform on Biodiversity and Ecosystem Services; Roy, H.E.; Pauchard, A.; Stoett, P.; Renard Truong, T.; Bacher, S.; Galil, B.S.; Hulme, P.E.; Ikeda, T.; Sankaran, K.V.; McGeoch, M.A.; et al. (Eds.) IPBES Secretariat: Bonn, Germany, 2023. [Google Scholar]
  118. Epanchin-Niell, R.S. Economics of Invasive Species Policy and Management. Biol. Invasions 2017, 19, 3333–3354. [Google Scholar] [CrossRef]
  119. Blumberga, D.; Muizniece, I.; Blumberga, A.; Baranenko, D. Biotechonomy Framework for Bioenergy Use. Energy Procedia 2016, 95, 76–80. [Google Scholar] [CrossRef]
  120. Harris, H.E.; Patterson, W.F.; Ahrens, R.N.M.; Allen, M.S.; Chagaris, D.D.; Larkin, S.L. The Bioeconomic Paradox of Market-Based Invasive Species Harvest: A Case Study of the Commercial Lionfish Fishery. Biol. Invasions 2023, 25, 1595–1612. [Google Scholar] [CrossRef]
Plants 13 01745 g001
Figure 1. (a) S. canadensis L. (photo by Mirela Uzelac Božac); (b) Widespread occurrence of invasive S. canadensis in Istria, Croatia (photo by Danijela Poljuha).
Figure 1. (a) S. canadensis L. (photo by Mirela Uzelac Božac); (b) Widespread occurrence of invasive S. canadensis in Istria, Croatia (photo by Danijela Poljuha).
Plants 13 01745 g001
Plants 13 01745 g002
Figure 2. Worldwide distribution of S. canadensis (taken from Popay and Parker [11]).
Figure 2. Worldwide distribution of S. canadensis (taken from Popay and Parker [11]).
Plants 13 01745 g002
Plants 13 01745 g003
Figure 3. Methodology for Solidago canadensis resource validation (scenarios testing) (adapted from Zihare and Blumberga [91] (Illustration created in Canva).
Figure 3. Methodology for Solidago canadensis resource validation (scenarios testing) (adapted from Zihare and Blumberga [91] (Illustration created in Canva).
Plants 13 01745 g003
Table 1. Sample type and geographical origin of Solidago canadensis, identification/quantification methods, phytochemical groups (including the number of identified compounds), with corresponding references.
Table 1. Sample type and geographical origin of Solidago canadensis, identification/quantification methods, phytochemical groups (including the number of identified compounds), with corresponding references.
Sample Type and OriginSeparation MethodIdentified CompoundsReference
Phytochemical GroupNo
Essential oils from leaves (Hungary)GC/MS Terpenoids 66[30]
Essential oils from inflorescences (Hungary)71
Essential oils from roots (Hungary)69
Essential oils from the green parts (Poland)GC-MS and NMRTerpenoids 16[31]
Essential oils from leaves at the vegetative stage (Russia, Moscow Main Botanical Garden)GC-MS15
Essential oils from leaves at the blooming stage (Russia, Moscow Main Botanical Garden)15
Essential oils from inflorescences (Russia, Moscow Main Botanical Garden)11
Essential oils from aerial parts (Moscow region, Krasnogorsk district)15
Essential oils from aerial parts (Austria)GC-MSTerpenoids 15[32]
Essential oils from aerial parts (Tver’ region)16
Essential oils from aerial parts (Penza region)14
Essential oils from aerial parts (Kazakhstan)15
Essential oils from aerial parts (Altaj region)15
Essential oils from aerial parts (Sakhalin region)14
Essential oils from aerial parts (Ukraine)15
Essential oils from aerial parts (Tula region)16
Essential oils from aerial parts (Slovakia)GC-MSTerpenoids 5[21]
Essential oils from leaves and inflorescences (China)GC-MSTerpenoids 6[33]
Essential oils from the whole plant (China)GC-MSTerpenoids 7[34]
Essential oils from aerial parts (Poland)GC-MSTerpenoids 6[35]
Essential oils from aerial parts (Poland)GC-MSTerpenoids 3[36]
Essential oils from aerial parts (Lithuania)GC-MSTerpenoids 6[37]
Air-dried herbs (Hungary)HPLC-MSFlavonoids 7[38]
Phenolic acids 2
Aerial parts (Poland)UPLC/ESI-MSFlavonoids 9[39]
Phenolic acids 9
Roots with rhizomes (Poland)Phenolic acids 9
Inflorescences and leaves (Slovakia)LC-MS/MSFlavonoids 8[40]
Phenolic acids 8
Flowers (Hungary)GC–MS Terpenoids50[41]
Compounds with benzene ring2
Open-chain alcohols, aldehydes, and ketones 3
Honey (Hungary)GC–MS Terpenoids42
Compounds with benzene ring 13
Open-chain alcohols, aldehydes and ketones 7
Lactones 2
Esters of open-chain acids 2
Fatty acids1
Open-chain and ringed, saturated and unsaturated hydrocarbons15
GC-MS = gas chromatography coupled with mass spectrometry, NMR = nuclear magnetic resonance, HPLC-MS = high-performance liquid chromatography coupled with mass spectrometry, UPLC/ESI-MS = ultra-performance liquid chromatography-electrospray tandem mass spectrometry. Values in the brackets indicate the number of identified individual compounds.
Table 2. The most abundant phenolic compounds in different extracts of Solidago canadensis herb (inflorescences and leaves). Numbers in square brackets indicate the references.
Table 2. The most abundant phenolic compounds in different extracts of Solidago canadensis herb (inflorescences and leaves). Numbers in square brackets indicate the references.
Polyphenolic GroupIdentified Individual CompoundsPresence of Compounds in the Extraction Solvent
Methanol EthanolAcetone Water Ether: ethanol
Phenolic acidsHydroxy-
benzoic acids
Plants 13 01745 i001		Gallic acid[40] [40]
Protocatechuic acid[40][40][40][40]
Vanillic acid [40][40]
Syringic acid[40] [40]
Hydroxy-
cinnamic acids
Plants 13 01745 i002
5-O-Feruloylquinic acid[39]
Caffeoyl-di-feruloylquinic acid[39]
1-Caffeoylquinic acid[39]
4-Caffeoylquinic acid[39]
5-Caffeoylquinic acid[39]
t-Ferulic acid[40][40][40][40]
Chlorogenic acid[38,39,40,48,49] [40][40][40,50]
Caffeic acid[38,40,51] [40]
3,4-O-Dicaffeoylquinic acid[39,52]
3,5-O-Dicaffeoylquinic acid[39,52]
Coumaric acid[40][40][40][40]
FlavonoidsFlavonols
Plants 13 01745 i003		Quercetin[38,39,40,48,49,51][40][40][40]
Quercitrin[38,39,40,48,49] [40][40][40,50]
Hyperoside[38,48,49]
Isoquercitrin[38,48,49] [50]
Rutin[38,39,40,48,49,51] [40][40][40,50]
Quercetin-O-hexoside[39]
Quercetin-(acetyl)-hexoside[48]
Quercetin-(rhamnosyl)- hexoside[48]
Quercetin-3-O-(6′-O-acetyl)-β-D-glucopyranoside [51]
Isorhamnetin 3-O-hexoside-7-O-deoxyhexoside[39]
Isorhamnetin-(acetyl)-hexoside [50]
Isorhamnetin-(rhamnosyl)-hexoside[51]
Isorhamnetin-3-O-β-D-glucopyranoside [51]
Kaempferol[39,40,49,51] [40][40][40,50]
Kaempferol-(rhamnosyl)-hexoside isomers[48]
Nicotiflorin[38] [50]
Hesperidin[40][40][40][40]
Afzelin[38,49]
Kaempferol-3-O-(6′-O-acetylyl)- β-D-glucopyranoside [51]
Kaempferol-3-O-β-D-apiofuranoside [51]
Kaempferol-O-hexoside-deoxyhexoside[39]
Flavanols
Plants 13 01745 i004		Epicatechin[40][40][40][40]
Catechin[40][40]
Flavanones
Plants 13 01745 i005		Hydroxy flavanone[40][40][40]
Disclaimer/Publisher’s Note: The statements, opinions and data contained in all publications are solely those of the individual author(s) and contributor(s) and not of MDPI and/or the editor(s). MDPI and/or the editor(s) disclaim responsibility for any injury to people or property resulting from any ideas, methods, instructions or products referred to in the content.

Share and Cite

MDPI and ACS Style

Poljuha, D.; Sladonja, B.; Uzelac Božac, M.; Šola, I.; Damijanić, D.; Weber, T. The Invasive Alien Plant Solidago canadensis: Phytochemical Composition, Ecosystem Service Potential, and Application in Bioeconomy. Plants 2024, 13, 1745. https://doi.org/10.3390/plants13131745

AMA Style

Poljuha D, Sladonja B, Uzelac Božac M, Šola I, Damijanić D, Weber T. The Invasive Alien Plant Solidago canadensis: Phytochemical Composition, Ecosystem Service Potential, and Application in Bioeconomy. Plants. 2024; 13(13):1745. https://doi.org/10.3390/plants13131745

Chicago/Turabian Style

Poljuha, Danijela, Barbara Sladonja, Mirela Uzelac Božac, Ivana Šola, Danijela Damijanić, and Tim Weber. 2024. "The Invasive Alien Plant Solidago canadensis: Phytochemical Composition, Ecosystem Service Potential, and Application in Bioeconomy" Plants 13, no. 13: 1745. https://doi.org/10.3390/plants13131745

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop