NC State
BioResources
Yucel, G. (2022). "Seed propagation, adaptation to cultivation conditions, determination of ornamental plant properties, and ex situ conservation of the endemic species Centaurea hermannii F. Hermann," BioResources, 17(1), 616-633.

Abstract

This study focused on seed propagation and ex situ conservation of the endemic species Centaurea hermannii F. Hermann. Plant properties such as vegetation cycle, adaptation to the cultivation environment, morphological characteristics of the plants and seeds, and esthetic properties as an ornamental variety were investigated. The percentage of viability of the seeds, as well as the effects of different seed germination methods when applied to the germination speed, were also explored. C. hermannii specimens planted in soil adapted quickly under field conditions and flowered over a period of two months, with a bright-orange color and glossy blossoms. In addition, the plants displayed all the type-specific botanical and esthetic properties, as well as provided value as an ornamental plant. An ex situ conservation area was created with the plants collected. To determine the best germination conditions for C. hermannii seeds, various methods were explored. Among these, a combination of 200 ppm of GA3 treatment during a three-month storage period at 4 °C, followed by cold-wet stratification at 4 °C for three months, produced the best results in terms of mean percentage germination (70.5 %) and mean germination speed (3 days).


Download PDF

Full Article

Seed Propagation, Adaptation to Cultivation Conditions, Determination of Ornamental Plant Properties, and Ex Situ Conservation of the Endemic Species Centaurea hermannii F. Hermann

Gül Yücel

This study focused on seed propagation and ex situ conservation of the endemic species Centaurea hermannii F. Hermann. Plant properties such as vegetation cycle, adaptation to the cultivation environment, morphological characteristics of the plants and seeds, and esthetic properties as an ornamental variety were investigated. The percentage of viability of the seeds, as well as the effects of different seed germination methods when applied to the germination speed, were also explored. C. hermannii specimens planted in soil adapted quickly under field conditions and flowered over a period of two months, with a bright-orange color and glossy blossoms. In addition, the plants displayed all the type-specific botanical and esthetic properties, as well as provided value as an ornamental plant. An ex situ conservation area was created with the plants collected. To determine the best germination conditions for C. hermannii seeds, various methods were explored. Among these, a combination of 200 ppm of GA3 treatment during a three-month storage period at 4 °C, followed by cold-wet stratification at 4 °C for three months, produced the best results in terms of mean percentage germination (70.5 %) and mean germination speed (3 days).

DOI: 10.15376/biores.17.1.616-633

Keywords: C. hermannii; Ex situ conservation; Ornamental plant characteristics; Cold-wet stratification

Contact information: Landscape and Ornamental Plants Program, Yalova Vocational High School, Yalova University, Yalova, Turkey; E-mail: gulyucel68@gmail.com

INTRODUCTION

Destruction of the natural environment, a rapid increase in the global population, unsustainable use of plant resources, and growing pollution in many different parts of the world have led to the threat of extinction of a large number of plant species by the end of the century (López-Pujol et al. 2006; Okay et al. 2011; Convention on Biological Diversity (CBD) 2018; Kırmızı et al. 2019). Therefore, supporting biodiversity has become an essential factor in conservation and sustainability. In addition, the recognition that biodiversity is a source of wealth has grown in the vast majority of countries around the world (Avcı 2008). Efforts to protect biodiversity and adopt sustainable measures have begun to attract the world’s attention (Carwardine et al. 2018; Locke et al. 2019). The Rio convention, on biological diversity, encourages all parties to the convention to recognize biological diversity and to take necessary measures to protect it (Ocak et al. 2017). Therefore, a variety of in situ and ex situ conservation methods have been explored to ensure the sustainability of biodiversity and to protect species in danger of extinction (Bürün 2021).

Propagating plants from seeds is an inexpensive and practical method for ex situ conservation of endangered plant species. One of the principal issues in the effective protection of endangered species is to adopt the necessary measures for the reproduction of these species (Okay et al. 2011). In addition to being a crucial propagation stage of seeds, germination is the first step in the vegetative phase of plants and is the priority concern for the recovery and sustainability of endangered species (Schnadelbach et al. 2016; Ganatsas et al. 2019; Kırmızı 2019; Erken 2021). Knowledge of both the germination percentage and germination period for existing plant seeds is directly related to the success of propagation techniques. Thus, determination of the most appropriate methods, in addition to specifying the germination properties of individual plant species, is critical for carrying out research in this area (Cesur et al. 2017; Uskutoğlu and Şenkal 2019).

The successful propagation of most plants requires the use of appropriate methods in the right environments. In this regard, natural plant-based designs have become increasingly popular in many countries, instead of using costly and unsustainable plans that do not adapt to a region’s ecology, climate, or natural structure. Governments agree on various regulations to encourage the utilization of natural plant species (Sağlam and Önder 2018). Natural plants are a target market for arboriculture producers and commercial dealers due to their environmental benefits (Anderson et al. 2021). However, the use of natural plants in horticultural designs is only possible if the properties of the individual species and their production methods are well known (Mikkelsen 1986; Von Henting 1998). According to Noroozi et al. (2019), endemism is an important criterion for the conservation of biodiversity both at the national and global level. Therefore, using endemic species as natural plants in horticultural designs makes leads to attractive results.

The genus Centaurea, which includes various producible and usable endemic species, is also remarkable. Turkey is the main center of species diversity for the Centaurea L.; the Centaurea genus is the third largest genus in Turkey. There are 217 species (146 endemic), 36 sub-species (22 endemic), and 28 varieties (16 endemic), and its percent endemism is 66.8% (Wagenitz 1975; Özhatay et al. 2011; Bona 2013, 2014).

Centaurea hermannii is a Euxine endemic species distributed in the northwest region of Turkey (Gürdal and Özhatay 2011). Bilz et al. (2011) noted that C. hermannii is an endemic species in Turkey and Bulgaria. While Ozhatay and Keskin (2007) and Eroglu et al. (2014) reported that the species is found only on the Çatalca Peninsula and Ömerli basin in Istanbul, Turkey. Uğurtaş et al. (2014) also located the species in the Delmece plateau of Yalova province. In general, the Centaurea hermannii F. Hermann is a simple, perennial, and vertical-growing herbaceous plant with a height of 30 to 60 cm. Its flowers are yellow-orange in color, and it flowers from June to July. Centaurea hermannii is an endemic species and grows in scrubs (maquis) and oak forests at altitudes of 100 to 500 meters (Yaltırık and Efe 1989; Akkemik 2017).

Özdemir and Ulus (2018) reported that some Centaurea species, such as Centaurea consanguinea, Centaurea hermannii, and Centaurea kilaea, are highly suitable for pollination yards, which are critical in supporting the decreasing population of pollinators, especially in urban areas, and for supporting urban biodiversity. Furthermore, Yankova-Tsvetkova et al. (2018) found that the distributions of some species of the genus Centaurea are considerably restricted and are represented by a single population. In this case, if there is habitat damage and population fragmentation, the species will be in danger of extinction. Its seeds could be infested with insects, and the percent germination of endemic species reduced, limiting their ability to regenerate, spread, and reproduce. However, Tel et al. (2019) suggested that the species C. hermannii possesses the right characteristics to become a potential ornamental plant.

The issues mentioned above make research on propagation necessary the genus Centaurea. This study discussed the endemic C. hermannii taxon, which is among the endangered (EN) species based on International Union for Conservation of Nature (IUCN) (2014) data. This study concentrated on determining the most appropriate method for propagation of C. hermannii from seeds under incubation conditions. The plants resulting from this process were planted either in pots or in soil in the research yard and monitored. Attempts were made to determine the species’ landscape characteristics, and the adaption potential of the species outside its natural population was assessed. However, the ultimate objective of this study was to cultivate, promote, and create a collection yard for ex situ conservation of C. hermannii.

EXPERIMENTAL

Materials

The seeds of C. hermannii F. Hermann, which constituted the parent material for this study, were collected from a natural population of plants in Delmece in the province of Yalova on 25 July 2019 (Fig. 1). The study was carried out under the climate conditions of Yalova province in 2019, 2020, and 2021 (Fig. 2). The laboratory, greenhouse, and field studies were performed in the following locations: seed germination studies and seedling growth stages were made at Yalova Vocational High School Research and Application Laboratory and Greenhouse facilities at Yalova University; and observations and measurement of the seedlings, which were planted in pots and in soil, were carried out in the Çınarcık research yard (Fig. 1). The soil characteristics of both Delmece and the research yard in Çınarcık, where plant cultivation studies were conducted, are provided in Table 1.

Fig. 1. Delmece natural area; general appearance of C. hermannii in the natural population; and Cınarcık research yard, Yalova

Fig. 2. Climate diagram showing the relationship between temperature and precipitation in Yalova province (Walter et al. 1975)

Table 1. Soil Characteristics of Delmece Natural Area and Çınarcık Research Yard

Methods

Determination of morphological and physiological characteristics and ornamental plant properties

Some of the seedlings were planted in the soil (60 plants) of the research yard, while others were planted in pots (60 plants) to evaluate the physiological and esthetic properties of the plants and to determine their adaptability to the cultivation conditions. Between April and August, the plants in both the Çınarcık research yard and Delmece (natural population) were monitored, and the necessary measurements and observations of the morphological characteristics (number of main shoods, main shoods length, number of side shoots, etc.) of the plant were recorded. In total, 3 viols with 104 compartments were used for all measurements, observations and ex situ conservation and 312 seedlings were planted.

104 seedlings tallied after the germination tests were planted in 104 vials containing peat (10 November 2019) and grown in unheated greenhouse conditions (average 14/9 °C day/ night temperature 70% RH and 3 times daily 10 s. mistpropagation application) in order to carry out observations and measurements on the seedlings placed into pots. Seedlings were transplanted into 8×8 cm square peat pots, depending on their stage of development (i.e., with 2 to 3 leaves). On 16 March 2020, the growing seedlings (with 6–7 leaves) were transferred to 16 x 13.5 cm pots filled with soil, the composition of which is listed in Table 1 (Çınarcık research yard) and the morphological characteristics of the plants (number of main shoods, main hoods length, number of side shoots, etc.) monitored appropriately. A similar method was also used to monitor the seedlings planted in the soil. The seedlings grown in 8×8 cm square pots were planted at 30 x 30 cm intervals in the yard soil (Çınarcık research yard), the composition of which is provided in Table 1 and monitored accordingly.

All observations, measurements, and evaluations of the plants’ morphological and physiological characteristics, and as well as their life cycle, were made in the natural population in Delmece, and in the seedlings planted in pots and in soil in the Çınarcık research yard. These data also generated preliminary information on the potential ornamental plant value of this species. Similarly, it was also possible to obtain information about the esthetic and functional properties of the plant for its potential use in landscape designs; To determine morphological characteristics, three groups of 10 plants each (30 plants in total), were set out randomly, and the following parameters and measuring/counting methods were carried out on the different species:

  • Number of main shoots: The number of above-ground main shoots on the plant (number).
  • Main shoot length: The distance from the ground to the most extreme flower on the shoot (cm).
  • Number of side shoots: The number of side shoots emerging from the plant’s main branches (number).
  • Average side-shoot length: The distance between the place on the main shoot where the side shoot emerges and the flower at its most extreme point (cm).
  • Number of buds: The total number of buds on the plant (number).
  • Main and side-shoot widths: The width of the most bulging part of the bud in millimeters. The buds were measured just before they developed color.
  • Bud height: The measurement from end to end of the longest portion of the bud in millimeters.
  • First blooming date: The date on which the first flower on the plant opened.
  • Last blooming date: The date when the last flower on the plant was completely shriveled.

Seeds were collected from the location with care to avoid harm to the endemic plant population. Using the method specified in Bacchetta et al. (2006), seeds were picked randomly and in minimum amounts. The collected seeds were cleaned and dried in a shaded place with an average temperature of 20 to 21 °C, where air flow was provided by ventilation devices. The study began on 5 August 2019 after the seeds had been left to dry for approximately ten days. The following measurements and observations were performed to determine the morphological and physiological characteristics of the seeds: seed size (width, height), 1000 kernel weight, the average number of seeds in 1 gram, seed maturation date, capsule splitting date, and seed shedding date. In addition, a seed viability test was conducted.

Seed viability test

Viability tests were carried out on 8 August 2019. Initially, the seeds were separated into three groups, each containing 20 seeds. Subsequently, the seeds were maintained in water at room temperature for 24 h, and then they were removed (from the water). After cutting 1/3 of the seeds, they were kept in 1% tetrazolium (2,3,5 Triphenyl tetrazolium chloride) (Merck, Darmstadt, Germany) solution at 30 °C for 24 h. Following these procedures, the seed boll was peeled. Based on their degrees of staining and physical observations, the seeds were classified as follows: viable (completely stained), semi-viable (less coloration or colorless patches on the seed), or nonviable (no coloration) (Moore 1985; Peters 2000).

Germination tests

Germination tests were made using 100×20 mm glass Petri dishes in a germination cabinet (Programmable Plant Growth Chamber SWGC-450; Daihan Scientific, Seoul, Korea). Before being placed into Petri dishes, the seeds were sterilized in 70% ethanol (Soltek, Turkey) for 1 min, after which they were treated for 10 min with a commercially available 20% solution containing 5.25% sodium-hypochlorite (BRTR Chemistry, İzmir, Turkey). Following sterilization, distilled water was used to purify the seeds. Petri dishes and blotting papers were sterilized for 30 min at 100 °C before use. Seeds were gently placed into Petri dishes on moist blotting papers in such a way that they did not contact each other. To prevent disease, a commercial fungicide containing the active ingredients Fludioxonil (25 g/L) + Metalaxyl-M (10 g/L) (Maxim XL 035 FS, Syngenta, Gaillon, France) was applied to the seeds in the Petri dishes at the level of 2.5 mL/L. Parafilm was used to cover Petri dishes with closed lids. When analyzing the germination studies, the final germination percentage (FGP) of the seeds was taken into consideration. In situations where light/dark conditions and temperatures were not specified, the 12/12-hour photoperiod and a temperature of 20±0.5 °C was assumed. A seed was considered to have germinated when a two-millimeter radicle had emerged from the seed shell. Counts were taken every two days, and radication was monitored for 30 days (Eser et al. 2005; ISTA 2013).

The conditions listed in Table 2 were used to determine the germination performance under light/dark conditions at different temperatures. Seeds were kept at a temperature of 10, 15, 20, or 25 °C and under light conditions of either constant light or constant dark. The research was carried out on 15 August 2019, and the light source had an intensity of 3400 lumens.

Table 2. Temperature, Light Applications, and Time Periods

As shown in Table 3, different conditions of temperature and light were used to determine the effects of three months storage at 4° C, cold-wet stratification, applications of Gibberellic acid (GA3) (Merck, Darmstadt, Germany), and the effects of these combinations on germination. The seeds were kept in paper bags and moist perlite for cold-wet stratification at 4 ℃ for three months, respectively. The GA3 treatments were carried out by soaking the seeds in a 200, 400, or 600 ppm GA3 solution for 24 h. After applying the relevant variables of temperature and light, the seeds were exposed to germination tests in Petri dishes in a climate cabinet under the following conditions: 70% humidity and 20 ± 0.5º C temperature under a 12/12 light regime.

Table 3. Applications of Storage (4 °C), Cold-Wet Stratification, and Their Combinations with Gibberellic Acid (GA3) and Dates

100 plants were reserved to create an ex situ conservation yard. On 18 March 2020, plants with sufficient growth (i.e., with 2 to 3 leaves) in 8×8 cm square pots were planted in the ex situ conservation yard at 30×30 cm intervals. On 16 March 2020, the extra plants that were not used in the collection yard, were planted within their natural populations for recovery.

Experimental design and data analysis

Experiments were designed by the Randomized Block Experimental Design with four replications, with each replication containing 50 seeds. Data obtained this experiment were analyzed with the IBM SPSS Statistics Base 22.0 (IBM Corp., Armonk, NY, USA) statistical program. The data were subjected to a one-way analysis of variance (ANOVA), with Duncan’s multiple comparison test applied to the treatments that were identified differentially. Germination percentages (%) were determined after counting and were subjected to the application of arc-sine data transformation.

RESULTS AND DISCUSSION

Plant, Flower, and Seed Properties of Centaurea hermannii

Table 4 shows the flower and plant features of C. hermannii plants grown in natural areas, in pots, and in the soil. Observations and measurements of the plants in the research yard showed a loss in the number of buds, in both pots and in the soil, at the end of the first year only. The fact that the plants were only one year old and had not yet completed their two-year development could explain this observation. Indeed, significant increases in all properties were observed among the plants cultivated in the field during the second vegetation period. Despite differences in soil structure, the plants grown in the soil fully adapted to the conditions in the field and developed their full ornamental plant properties, especially in their second year, compared to those plants in the natural area. During the two-year period, buds generated a succession of flowers, one after the other, and the plants remained in bloom for about two months. In terms of the flowering period, the present observations are in line with those of Akkemik (2017), who noted that C. hermannii blooms in June-July. In terms of landscape value, however, the most significant characteristic of C. hermannii is undoubtedly its bright orange flowers, a feature that increases the esthetic properties of the plant. Özdemir and Ulus (2018) defined C. hermannii as an endemic plant that grows naturally in Istanbul and in pollinated yards. Tel et al. (2019) reported that C. hermannii ‘is a potential candidate for growing in parks and gardens, given its ornamental, orange-colored flowers and suitable height.’ In this work, C. hermannii was observed to be a reliable biennial ornamental plant that would flourish in parks and gardens. It should also be noted that, depending on the development of the plant, the attractiveness of C. hermannii continues to increase, especially in the second year.

Table 4. Properties Related to the Structure of Flowers and Plants Grown in a Natural Population (Delmece), in Pots, and in Soil (Çınarcık research yard)

Morphological Characteristics of the Seeds

C. hermannii seeds are yellowish-brown in color and slightly tapered at the tip. In the direction of the tip section, the color noticeably changes to yellow. At the top of the seed, villiform structures are arranged in a brush form.

Table 5 summarizes the data obtained from measuring, counting, and weighing of C. hermannii seeds. On average, each gram contained 114.69 seeds. Average seed height and width was found to be 5.27 and 2.37 millimeters, respectively. The net viability percentage of seeds was identified as 72.2% in the tests performed. In addition, the seed viability percentage of C. hermannii was observed to be low in the year the study was conducted. The high proportion of semi-viable seeds suggested that there could have been damage from insects, harm due to physical impacts, and seed maturation issues. However, the net non-viable seed percentage was considered to be within acceptable limits (Fig. 3).

Table 5. Seed Properties of Centaurea hermannii

 

Fig. 3. Appearance of viable, semi-viable and non-viable seeds in Centaurea hermannii

The average seed height and width were 5.27 and 2.37 millimeters, respectively. Several studies, including those by Gürdal and Özhatay (2010), Eroğlu et al. (2014), and Tel et al. (2019) reported 4 to 5 mm of seed height of C. hermannii. These results also support the measurements found in this study. In addition, there was 72.2% seed viability percentage in C. hermannii. This value was reported differently among Centaurea species. For instance, Ozel et al. (2006) reported as 85% in C. tchihatcheffii species, Kurt and Erdağ (2009) as 98% in C. zeybekii species, Emek and Erdağ (2012) as 80% in Rhaponticoides mykalea species, Atasagun and Aksoy (2018) as 82% in C. amaena species, and Yankova-Tsvetkova et al. (2018) as 17.5% in C. achtarovii species, respectively. Therefore, the seed viability percentages could vary significantly among the species. In addition, due to environmental conditions such as climate, soil, and insect damage, variations might even occur among seeds of the same species.

In this study, it was observed that the fruits started to ripen proximately 60 days after the first blooming in the culture medium, the seed capsules began to crack after 60-70 days, and the seeds were shed to a large extent after 75 days (Table 6). However, in the natural area, the fruits began to ripen 60 days after the first blooming the fruit began to ripen, and the capsules split approximately 65 to 70 days later. Furthermore, both in the cultivation environment and natural area, the capsules were observed to be shedding their seeds quickly after reaching the maturation stage. The findings suggest that 70 to 80 days after the first blooming are the most suitable period for collecting C. hermannii seeds.

Table 6. Periods of Fruit Ripening, Capsule Splitting, and Seed Shedding of the Plants Grown in the Natural Population (Delmece), in Pots, and in Soil (Çınarcık research yard)

Determination of Seed Germination Performances at Different Temperatures and Light/Dark Conditions

Germination Percentage

When only the percent germination is taken into account while evaluating the effects of different temperature and light applications on the seed germination of C. hermannii, there was no statistical difference among the following applications: 8.00% percent germination at 10 ℃ and in dark condition, 7.00%, 8.00%, and 8.00% in the full-light application and at 10, 15, and 20 ℃, respectively; and all four applications were classified in the first group. Although some applications produced partially positive results, it would be plausible to say that the germination percentages for all applications remained at a significantly low level when three different temperatures and two constant light conditions were taken into consideration (Table 7).

Various studies in the literature reported germination temperatures and light conditions used in different Centaurea species. For instance, while Abbasian et al. (2017) proposed a 20 ℃ temperature for optimum germination of C. balsamita, Türkoğlu et al. (2009) suggested that 15 ℃ was suitable for three different species: C. balsamita, C. virgata, and C. iberica. However, Albert et al. (2002) stated that the highest germination percentage in C. pinnata was observed at a constant temperature range of 15 to 20 ℃, and a constant temperature of 15 ℃ generated a significant effect on the germination percentage when compared to the variable temperature regime of 15/25 ℃. Similarly, Pitcairn et al. (2002) determined that 20 ℃ was the only constant temperature, and the varying temperature regime of 15/25 ℃ further supported the optimum germination rate for C. calcitrapa. Therefore, studies carried out with varying Centaurea species also supported this study results.

Zare et al. (2020) suggested that a suitable germination temperature was 25 °C for C. bruguierana species. In this study, while the emerging opinion that constant light for C. hermannii seeds has a negative effect on the percentage and speed of germination, Valletta et al. (2016) reported that C. cineraria subsp. circae had the highest germination percentage at a temperature of 20/10 °C and a 12/12 photoperiod application (67.5%). Similarly, Uysal et al. (2006) identified that 16/8 h of light/dark at 25 °C produced better results than 8/16 h of light/dark applications in C. tomentella. Furthermore, Nosratti et al. (2017a) reported that in C. iberica, the highest germination percentage was recorded at varying temperatures of 15/25 °C and 16/8 h of light/dark conditions. They also stated that light had a stimulating effect on seeds when compared to constant dark conditions. They further determined in C. cyanus that light at high temperatures positively affected the germination percentage; however, low temperatures negatively affected it. Therefore, these reports supported the findings that full-light resulted in a significant difference in the germination percentage at 15 to 20 °C.

In this study, when the germination percentage was considered, light had no effect at 10 °C; however, it positively affected germination at 15 and 20 °C, and the full-light application additionally provided better results on the percentage of germination. However, further increments in temperature reversed the situation, as the temperature reached 25 °C. This result suggests that higher temperatures above a certain level reduces the light effect on the percentage of germination in C. hermannii. In C. diffusa Lam 20 °C and 20 to 30 °C dark, and 20 to 30 °C light/dark conditions had a lesser effect on percentage of germination when compared to 15 °C and dark conditions (Buhler and Hoffman 1999; Türkoglu et al. 2009). Demirel et al. (2017) also reported that Centaurea sp. plants had a long vegetation period. Nosratti et al. (2017b) reported that while the best germination percentage was observed at 25 °C in C. balsamita taxon, the light and dark conditions had similar effects on seed germination of C. balsamita. Noting that the responses of different Centaurea species to the light period were not comparable, Köse and Yücel (2015) monitored varying photoperiod conditions and germination percentages at 25 °C in four different Centaurea taxa. Accordingly, C. aphrodisea and C. luschaniana were not affected by any light conditions, and C. amaena increased its germination percentage with an increased exposure time. However, the percentage of germination of C. lycia decreased with low light exposure.

Germination speed

Table 4 shows the germination speed of C. hermannii seeds under various temperature and light conditions. In terms of germination speed, the best results were obtained from 20.00 days of full-light at 15 °C 19.33 days of full-dark at 20 °C, and 26.00 days of full-dark at 25 °C. However 10 °C was found to delay the germination speed both in dark and light conditions. Hence, it can be speculated that the constant-dark condition may result in a significant slowdown in the germination percentage at 10 °C. When the temperature was raised to 15 to 20 °C, an increase in germination speed was also observed. Similarly, Turkoglu et al. (2009) stated that the maximum germination speed in C. balsamina was observed at 15 °C. However, when the study results were evaluated collectively, the constant light and temperature combinations did not provide the expected outcomes in germination speed.

Table 7. Effects of Different Temperature and Light Conditions on the Seed Germination of Centaurea hermannii

Determination of the Effects of Three Months of Storage at 4 °C, Cold-Wet Stratification, Gibberellic Acid (GA3) or their Combinations on Germination

Percentage of germination

When the effects of three months storage at 4 °C, cold-wet stratification, and GA3 treatments were evaluated on the germination of C. hermannii seeds (Table 8), the best result in terms of percentage of germination was recorded as 70.5% in the applications of three months storage at 4 °C + cold-wet stratification + 200 ppm GA3. It was noteworthy that among the applications, storage at 4 °C for three months without GA3 treatment + cold-wet stratification resulted in a low percentage of germination. In other applications, it seemed that the GA3 treatment tolerated the negative effect of cold-wet stratification.

Germination speed

In terms of germination speed, storage at 4 °C for three months + cold-wet stratification + 200 ppm GA3 treatment yielded the best results. The considerable difference in germination speeds between the groups with and without cold-wet stratification indicated that cold-wet stratification increased germination speed.

Considering the data specified in the literature for both parameters, Okay and Günöz (2009), Okay et al. (2011), and Okay and Demir (2021) noted that stratification for 120 to 150 days and application of 100 ppm GA3 before planting increased the seed germination percentage in C. tchihatcheffii. Similarly, Eddleman and Romo (1988) reported that cold-wet stratification shortened the seed germination period; however, it increased total germination in C. maculosa Lam. Saba et al. (2017) indicated that the GA3 treatment in seeds increases germination in C. balsamita Lam. In his germination study with C. diffusa and C. maculosa, Nolan (1989) also stated that the GA3 is a robust stimulant, and some seeds in a dormant state treated with cold at 3 °C successfully germinated at 25 °C. However, Luna et al. (2008) indicated that cold stratification did not result in a significant effect on seed germination of C. ornata and C. pinae. According to Aghilian et al. (2014), a six-day precooling treatment at 4 °C had no influence on the germination process in C. cyanus. As a result, depending on the species, responses of Centaurea seeds to various applications could provide notably different results.

Elias et al. (2012) and Baskin and Baskin (2014) reported that germination qualities of plant species could vary greatly based on genetic and environmental factors, as well as the media used in germination tests. Some researchers suggested that seed germination percentages could be altered depending on the fruit the seed came from or where the seeds were collected from the plant (Nielsen 1987; Copeland and McDonald 2001). Another explanation for disparities in results across studies could be differences in seed storage conditions, which could alter germination during the time between seed harvest and germination (Probert 2000). Therefore, Gresta et al. (2010) noted that germination is a complex physiological process that could be affected by many factors.

Table 8. Effects of Storage for Three Months at 4 °C, Cold-Wet Stratification, and GA3 Treatments on Germination of Centaurea hermannii Seeds

Creation of an ex situ conservation yard

During the study, the seeds that germinated were removed from the Petri dishes and planted in vials in the peat medium. The seedlings grown in vials up to 2–3 leaflets were re-planted in 8×8 cm square pots containing peat, and then, they were transferred to the ex situ conservation yard in outdoor conditions at the beginning of March (Fig. 4).

Recovering plants to the natural population

The redundant plants, which were not used in the collection yard, were transferred to their natural populations in mid-March (Fig. 4).

Fig. 4. a) The ex situ conservation yard built by cultivated C. hermannii; b) the appearance of the plant grown in the soil; c) the appearance of the plant flower

CONCLUSIONS

  1. Based on the results of this study, C. hermannii is suitable in both ecological and landscape designs. In addition, it was determined that the plants are able to adapt to the cultured conditions without any difficulty, and that it even grows more spectacular as it adapts to the area. This finding suggests that C. hermannii could be used as a potential ornamental plant in landscape designs.
  2. For the plant’s generative production, temperature and light requirements for germination were specified in detail. Cold-wet stratification and GA3 treatments 200 ppm of GA3 treatment during a three-month storage period at 4 °C, followed by cold-wet stratification at 4 °C for three months resulted in high germination percentages. In addition, it was observed that cold-wet stratification could shorten the germination time when combined with GA3 treatment.
  3. An ex situ conservation yard for C. hermannii was built with the plants gathered from the study. The results of the study showed that the ex situ conservation could be achieved for C. hermannii by seed production.
  4. When needed, the plants could be grown easily under cultured conditions and used to restore damaged natural areas. The high percentages of germination of this species would enable rapid production of this species under cultured conditions.

ACKNOWLEDGMENTS

The authors thank to the Administration of Yalova University for their financial support and Yalova Branch Directorate Yalova for Nature Conservation and National Parks for their support in the fieldwork.

REFERENCES CITED

Abbasian, A., Asadi, Gh. A., and Ghorbani, R. (2017). “The effect of temperature on some germination index of invasive plant of Centaurea balsamita and determination of its germination Cardinal Temperatures,” Iranian Journal of Seed Science and Technology 5(2) 215-222.

Aghilian, S., Khajeh-Hosseini, M., and Anvarkhah, S. (2014). “Evaluation of seed dormancy in forty medicinal plant species,” International Journal of Agriculture and Crop Sciences 7(10), 760-768.

Akkemik, Ü. (2017). İstanbul’un Doğal Bitkileri (1. b.), Çevre ve Kültür Değerlerini Koruma ve Tanıtma Vakfı, İstanbul.

Albert, M. J., Iriondo, J. M., and Perez-Garcia, F. (2002). “Effects of temperature and pretreatments on seed germination of nine semiarid species from NE Spain,” Israel Journal of Plant Sciences 50(2),103-112.

Anderson, A. G., Messer, I., and Langellotto, G. A. (2021). “Gardeners’ perceptions of northwestern us native plants are influenced by ecological information and garden group affiliation,” HortTechnology 1, 1-14. DOI: 10.21273/HORTTECH04770-20

Atasagun, B., and Aksoy A. (2018). “Autecology and conservation biology of Centaurea amaena (Asteraceae),” Journal of Animal and Plant Sciences 28(1), 208-214.

Avcı, M. (2008). “Kentsel biyoçeşitlilik açısından bir değerlendirme: İstanbul örneği,” Kentsel Ekoloji ve Yaşanabilir Kent Sempozyumu, 81-105.

Bacchetta, G., Fenu G., Mattana E., Piotto B., and Virevaire M. (2006). “Manuale per la raccolta, studio, conservazione e gestione ex situ del germoplasma [Manual for the collection, study, preservation and management of ex situ germplasm]. Roma: APAT – Agenzia per la protezione dell’ambiente e per i servizi tecnici,” Manuali e Linee Guida 37, 248.

Baskin, C. C., and Baskin, J. M. (2014). Seeds: Ecology, Biogeography, and Evolution of Dormancy and Germination, Elsevier/Academic Press, San Diego.

Bilz, M., Kell, S. P., Maxted, N., and Lansdown, R. V. (2011). European Red List of Vascular Plants, Publications Office of the European Union, Luxembourg.

Bona, M. (2014). “New floristic records of Centaurea S.l. (Asteraceae) for 27 squares in the flora of Turkey,” Hacettepe J. Biol. & Chem. 42(3), 331-335.

Bona, M. (2013). “An overview to Centaurea s.1. (Asteraceae) based on herbarium specimens of ISTE,” Istanbul Ecz. Fak. Dergisi 43(2), 121-137.

Buhler, D. D., and Hoffman, M. L. (1999). Andersen’s Guide to Practical Methods of Propagating Weeds & Other Plants, Weed Science Society of America, Lawrence, KS, USA.

Bürün, B. (2021). “Bitki biyoçeşitliliğinin korunmasında biyoteknolojinin kullanımı ve Türkiye’deki çalışmalar,” Eskişehir Teknik Üniversitesi Bilim ve Teknoloji Dergisi-C Yaşam Bilimleri ve Biyoteknoloji 10(1) 1-16. DOI: 10.18036/estubtdc.590752

Carwardine, J., Martin, T. G., Firn, J., Reyes, R. P., Nicol, S., Reeson, A., Grantham H. S., Stratford D., Kehoe L., and Chadès, I. (2018). “Priority threat management for biodiversity conservation: A handbook,” Journal of Applied Ecology 56(2), 481-490. DOI: 10.1111/1365-2664.13268

CBD (2018). Decision Adopted by The Conference of The Parties to The Convention on Biological Diversity, Convention on Biological Diversity, Sharm-El-Sheikh, Egypt, 30 November 2018 (CBD/COP/DEC/14/34).

Cesur, C., Coşge Şenkal, B., Uskutoğlu T., Yaman C., and Yurteri T. (2017). “Pıtrak (Xanthium itrumarium L.) tohumlarının en uygun çimlendirme metotlarının belirlenmesi üzerine bir araştırma,” TÜTAD 4 (2) 124-130.

Copeland, L. O., and McDonald, M. B. (2001). Principles of Seed Science and Technology, 4th Edition, Springer Science+Business Media, New York.

Demirel, S., Türkoğlu, N., and Özdemir, F.A. (2017). “Comparison of germination abilities of Centaurea sp. under in vivo and in vitro conditions,” Journal of Nutrition and Internal Medicine 19(1).

Eddleman, L. E., and Romo, J. T. (1988). “Spotted knapweed germination response to stratification, temperature, and water stress,” Canadian Journal of Botany 66(4).

Elias, S. G., Copeland, L. O., and McDonald, M. B. (2012). Seed Testing-Principles and Practices, Michigan State University Press, East Lansing, MI, USA.

Emek, Y., and Erdağ B. (2012). “Kritik tehlike altındaki endemik bitki Rhaponticoides mykalea (Hub.-Mor.)’nın ın vitro tohum çimlenmesi üzerine araştırmalar,” Nevşehir Üniversitesi Fen Bilimleri Enstitüsü Dergisi 1(2), 46-59.

Erken, K. (2021). “Investigation of vegetative properties and generative production of the potential ornamental and narrow endemic species Verbascum yurtkuranianum (Scrophulariaceae) for ex situ conservation,” BioResources 16(4), 7530-7549.

Eroğlu, H. K., Ozyigit I. I., Altay V., and Yarcı, C. (2014). “Autecological characteristics of Centaurea hermannii F. Herm an endemic species from Turkey,” Bulgarian Journal of Agricultural Science 20(1), 183-187.

Eser, B., Saygılı, H., Gökçöl, A., and İlker, E. (2005). Seed Science and Technology (Publication No. 3), (Vol.I-II), Ege University Seed Technology Application and Research Center, Izmir, Turkey.

Ganatsas, P., Tsakaldimi, M., Damianidis, C., Stefanaki, A., Kalapothareas, T., Karydopoulos, T., and Papapavlou, K. (2019). “Regeneration ecology of the rare plant species V. dingleri: Implications for species conservation,” Sustainability 11, 3305. DOI: 10.3390/su11123305

Genç, M. (2005). Ornamental Plants Growing (Volume 1, Publication No: 55), Süleyman Demirel University Faculty of Forestry, Isparta, Turkey.

Gresta, F., Cristaudo, A., Onofri, A., Restuccia, A., and Avola, G. (2010). “Germination response of four pasture species to temperature, light, and post-harvest period,” Plant Biosyst 144(4), 849-856.

Gürdal, B., and Özhatay N. (2011). “Taxonomical anatomical and karyological remarks on two endemic Centaurea L. species in Turkey: C. kilaea Boiss., C. hermannii F. Hermann,” Journal of Pharmacy of Istanbul University 41 104-120.

Hartman, T. H., Kester, E. D., and Davies, T. F. (1990). Plant Propagation Principles and Practices (5th Ed.), Prentice Hall Inc., Englewood Cliffs, NJ, USA.

ISTA (International Seed Testing Association) (2013). International Rules for Seed Testing, Bassedorf, Switzerland.

Kırmızı, S., Arslan, H., and Güleryüz, G. (2019). “Soğuk stratifikasyon uygulamalarının endemik Muscari bourgaei tohumlarında çimlenme üzerine etkisi – The effects of cold stratification treatments on the germination of endemic Muscari bourgaei seeds,” in: International Ornamental Plants Congress, Bursa, Turkey, pp. 46-50.

Kırmızı, S. (2019). Alpin Bitkilerde Dormansi ve Çimlenme, In Mathematıcs and Natural Scıences-2019/2, Cetinje-Montenegro.

Köse, Y. B., and Yücel, E. (2015). “Light effects on seed germination of endemic Centaurea L. species in section Phalolepıs (Cass.) DC.,” Biological Diversity and Conservation 8(3), 218-222.

Kurt, S., and Erdağ, B. (2009). “In vitro germination and axillary shoot propagation of Centaurea zeybekii,” Biologia 64, 97-101.

Locke, H., Ellis, E. C., Venter, O., Schuster, R., Ma, K., Shen, X., Woodley, S., Kingston, N., Bhola, N., Strassburg B. B. N., Paulsch. A., Williams, B., and Watson, J. E. (2019). “Three global conditions for biodiversity conservation and sustainable use: An implementation framework,” National Science Review 6(6), 1080-1082. DOI: 10.1093/nsr/nwz136

López-Pujol, J., Zhang, F. M., and Ge, S. (2006). “Plant biodiversity in China: Richly varied, endangered, and in need of conservation,” Biodiversity & Conservation 15(12), 3983-4026. DOI: 10.1007/s10531-005-3015-2

Luna, B., Perez, B., Cespedes, B., and Moreno, J. M. (2008). “Effect of cold exposure on seed 58 plant species comprising several groups from a mid-mountain Mediterranean area,” Ecoscience 15(4), 478-484.

Mikkelsen, J. C. (1986). “Commercial aspects of new crop development,” Symposium on the Development of New Floricultural Crops, XXII IHC 205, 49-56.

Moore, R. P. (1985). Handbook on Tetrazolium Testing, International Seed Testing Association, Zurich.

Nielsen, K. K. (1987). “Dormancy in seeds from different positions on individual plants,” in: International Symposium on Propagation of Ornamental Plants 226 255-262.

Nolan, D. G. (1989). Seed Germination Characteristics of Centaurea diffusa and C. maculosa, Doctoral Dissertation, The University of British Columbia.

Noroozi, J., Talebi, A., Doostmohammadi, M., Manafzadeh, S., Asgarpour, Z., and Schneeweiss, G. M. (2019). “Endemic diversity and distribution of the Iranian vascular flora across phytogeographical regions, biodiversity hotspots and areas of endemism,” Scientific Reports 9(1), 1-12.

Nosratti, I., Abbasi R., Bagheri, A., and Bromandan, P. (2017a). “Seed germination and seedling emergence of Iberian starthistle (Centaurea iberica),” Weed Biology and Management 17(3), 144-149.

Nosratti, I., Soltanabadi, S., Honarmand, S. J., and Chauhan, B. S. (2017b). “Environmental factors affect seed germination and seedling emergence of ınvasive Centaurea balsamita,” Crop & Pasture Science 68, 583-589.

Ocak, A., Öztürk, D., and Kara, G. (2017). Bilecik Florası, Turkuvaz Haberleşme ve Yayıncılık, ISBN 978-60565470-8-9.

Okay, Y., and Demir, K., (2021). “Centaurea tchihatcheffii Fisch. and Mey: An endangered endemic species found around Golbasi district of Ankara province, Turkey,” Advanced Journal of Environmental Science and Technology 12(1), 1-6.

Okay, Y., and Günöz, A., (2009). “Gölbaşı’na endemik Centaurea tchihatcheffii Fisch. et Mey. tohumlarının çimlenmesi üzerine bazı uygulamaların etkisi,” Tarım Bilimleri Dergisi 15(2) 119-126.

Okay, Y., Günöz, A., and Khawar, K. M. (2011). “Effect of cold stratification pretreatment and ph level on germination of Centaurea tchihatcheffii Fisch. et Mey. Seeds,” African Journal of Biotechnology 10(9), 1545-1549.

Ozel, C. A., Khawar, K. M., Mirici, S., Ozcan, S., and Arslan, O. (2006). “Factors affecting in vitro plant regeneration of the critically endangered Mediterranean knapweed (Centaurea tchihatcheffii Fisch et. Mey),” Naturwissenschaften 93(10), 511-517.

Özdemir, A., and Ulus, A. (2018). “Kent ekolojisine farklı bir yaklaşım: Tozlaşma bahçeleri,” Inonu University Journal of Art and Design 17-28.

Özhatay, F. N., Kültür, Ş., and Gürdal, M.B. (2011). “Check-list of additional taxa to the supplement Flora of Turkey V,” Turkish Journal of Botany 35(5), 589-624.

Özhatay, N., and Keskin, M. (2007). Ömerli Havzasının ‘İstanbul’Doğal Bitkileri.  WWF Türkiye Doğal Hayatı Koruma Derneği Vakfı, İstanbul.

Peters, J. (2000). Tetrazolium Testing Handbook: Contribution No. 29 to The Handbook on Seed Testing, Association of Official Seed Analysts, Inc., Lincoln, NE, USA.

Pitcairn, M. J., Young, J. A., Clements, C. D., and Balciunas, J. (2002). “Purple starthistle (Centaurea calcitrapa) seed germination,” Weed Technology 16(2), 452-456.

Probert, R. J. (2000). “The role of temperature in the regulation of seed dormancy and germination,” in: Seeds: The Ecology of Regeneration in Plant Communities, 2nd Edition, CAB International, Wallingford, pp. 261-292.

Saba, Y., Hassan, A., Iraj, N., and Sohbat, B. (2017). “Evaluation the effects of different factors on the seed germination and dormancy-breaking of knapweed (Centaurea balsamita Lam.),” Iranian Journal of Weed Science 13(1), 89-96.

Sağlam, C., and Önder, S. (2018). “The use of native halophytes in landscape design in The Central Anatolia, Turkey,” Turkish Journal of Agriculture-Food Science and Technology 6(12) 1718-1726.

Schnadelbach, A., Veiga-Barbosa, L., Ruiz, C., Pita, J.M., and Pérez-García, F. (2016). “Dormancy breaking and germination of Adenocarpus desertorumAstragalus gines-lopezii and Hippocrepis grosii (Fabaceae) seeds, three threatened endemic Spanish species,” Seed Science and Technology 44(1), 1-14.

Tel, M., Özhatay, F. N., and Keskin, M. (2019). İstanbul İli – Çatalca Peygamber Çiçeği (Centaurea hermannii) Tür Eylem Planı.

Turkoglu, N., Alp, Ş., and Cıg, A. (2009). “Effect of temperature on germination biology in Centaurea species,” African Journal of Agricultural Research 4(3), 259-261.

Uğurtaş, İ. H., Kaynak, G., Yılmaz, Özer, Kankılıç, T., Tuncalı, T., Emiroğlu, O., Çakır, D. T., Güvenç, Ş., Varlı, S. V., Çekici, T., Yıldırım, B., Aksu, S., Başkurt, S., and Arslan, M. (2014). Yalova Şube Müdürlüğü Ulusal Biyolojik Çeşitlilik Envanter ve İzleme Sonuç Raporu, Orman ve Su İşleri Bakanlığı Doğa Koruma ve Milli Parklar Genel Müdürlüğü, Yalova.

Uskutoğlu, T., and Şenkal, B. C. (2019). “Lamiaceae (Ballıbabagiller) familyasına ait bazı taksonların tohumla çoğaltım potansiyellerinin değerlendirilmesi – Evaluation of Seed Propagation of Some Taxon on Lamiaceae (Ballıbabagiller) Family,” in: International Ornamental Plants Congress – VII.Süs Bitkileri Kongresi, Bursa, Turkey.

Uysal, I., Celik, S., and Ozkan, K. (2006). “Studies on the germination of an endemic species Centaurea tomentella Hand.-Mazz.,” Pakistan Journal of Botany 38(4), 983-989.

Valletta, A., Santamaria, A. R., Fabrini, G., Tocci, N., Filho, V. C., Wagner, T., Brasili, E., and Pasqua, G. (2016). “Strategies for ex situ conservation of Centaurea cineraria subsp. circae (Asteraceae), an endemic plant from Lazio (Italy),” Plant Biosystems-An International Journal Dealing with all Aspects of Plant Biology 150(2), 323-332.

Von Henting, W. U. (1998). “Strategies of evaluation and introduction of new ornamental plants,” Acta Horticulturae 454, 65-80.

Wagenitz, G. (1975). “Centaurea L.,” in: Flora of Turkey and the East Aegean Islands, P. H. Davis (ed.), Edinburgh University Press, Edinburgh, Scotland.

Walter, H., Harnickell, E., and Mueller-Dombois, D. (1975). “Climate diagram maps,” Ind. Countries and the ecological climatic regions of the earth. Suppl. to the veg. monographs, 8 (11) 1-36.

Yaltırık, F., and Efe, A. (1989). Otsu bitkiler sistematiği Ders Kitabı, İstanbul Üniversitesi Fen Bilimleri Enstitüsü Yayınları.

Yankova-Tsvetkova, E., Ilieva, I., Stanilova, M., Stoyanov, S., and Sidjimova, B. (2018). “Reproductive biology of the endangered Bulgarian endemic Centaurea achtarovii (Asteraceae),” Biologia (Bratislava) 73(12) 1163-1175.

Zare, A., Deris, F., and Karimi, Z. (2020). “The evaluation of seed germination behavior of Centaurea bruguierana Hand.-Mazz to environmental factors,” Iranian Journal of Weed Science 16(2).

Article submitted: October 21 2021; Peer review completed: November 21, 2021; Revised version received and accepted: November 29, 2021; Published: December 3, 2021.

DOI: 10.15376/biores.17.1.616-633