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Australian Journal of Botany Australian Journal of Botany Society
Southern hemisphere botanical ecosystems
RESEARCH ARTICLE (Open Access)

The response of Nassella trichotoma (serrated tussock) seeds and seedlings to different levels of fire intensity

Talia Humphries https://orcid.org/0009-0003-9438-8367 A B and Singarayer Florentine https://orcid.org/0000-0002-5734-3421 B C *
+ Author Affiliations
- Author Affiliations

A Department of Rangelands, Wildlife and Fisheries Management, Texas A&M University, College Station, TX, USA.

B The Future Regions Research Centre, Institute of Innovation, Science and Sustainability, Federation University Australia, Mount Helen, Vic., Australia.

C Applied Chemistry and Environmental Science School of Science, STEM College, RMIT University, 124 La Trobe St, Melbourne, Vic. 3000, Australia.

* Correspondence to: s.florentine@federation.edu.au

Handling Editor: James Camac

Australian Journal of Botany 71(4) 188-198 https://doi.org/10.1071/BT22078
Submitted: 21 July 2022  Accepted: 3 April 2023   Published: 3 May 2023

© 2023 The Author(s) (or their employer(s)). Published by CSIRO Publishing. This is an open access article distributed under the Creative Commons Attribution-NonCommercial-NoDerivatives 4.0 International License (CC BY-NC-ND)

Abstract

Context: Fire is an important disturbance regime in grassland communities, since it is responsible for stimulating the regeneration of many species and for maintaining levels of biodiversity. When invasive plants, such as Nassella trichotoma, establish and become widespread in a grassland community, these important fire events can be altered in intensity and frequency, which means that they are able to facilitate the establishment of the exotic species. Therefore, before fire can be recommended as a suitable control technique for invasive species, or alternatively to be integrated into grassland restoration programs, understanding the response of the seeds of exotic species to high temperatures, such as those experienced during a fire, should be well understood.

Aims: Our aim was to identify their response to a gradient of temperatures associated with different levels of fire intensity. We examined how increased duration of exposure affects their response, and whether seed age or seed moisture content affect the germination response of this species.

Methods: To gain a fuller understanding of the fire response of N. trichotoma’s seedbank, seeds were collected in 2016, 2017, 2018 and 2019 and then stored until the commencement of the experiments in 2020. Selected seeds were first subjected to an increasing temperature gradient (80°C, 100°C, 120°C, 140°C, and a control), and an increasing duration of exposure (of 1, 3, 6, and 9 min). In the second experiment, one population was selected to test these same temperatures and duration of exposure after the seeds were hydrated to 15%, 50%, or 95%. Last, seedlings were grown for 3 months under glasshouse conditions and then exposed to increasing temperatures (20°C, 60°C, 80°C, 100°C, and 120°C), and an increasing duration of exposure (3, 6, and 9 min). The seedlings were assessed 2 weeks after the heat exposure for signs of damage.

Key results: It was found that increased temperatures and duration of exposure had a subtle negative effect on germination parameters, including reduced total germination and increased time to 50% germination. The 140°C treatment was seen to be a significant threshold because it killed all the seeds at any duration of exposure. A significant difference among the ages of each seed lot was observed to be a factor on the tested germination metrics, with the oldest tested population (2016) demonstrating the highest germination percentage, uniformity, and rate. Seed germination percentage was significantly reduced for seeds hydrated to 95% compared with the control treatment, whereas no significant difference was observed for the seeds hydrated to 15% and 50%. For the heat treatment of the seedlings, damage to the leaves was observed in the 80°C, 100°C, and 120°C treatments, with some plants in the 120°C treatment experiencing extensive damage prior to resprouting. No seedlings were killed at the tested temperatures.

Conclusions: Results of this study indicated that fire may be a useful tool for reducing seedbank density by killing a high proportion of the seeds on the soil surface, or located within the top 1 cm of the soil profile, but not for seeds buried more deeply. Efficacy of fire on surface and shallow-buried seeds is improved with high seed moisture content; however, these seeds buried below this depth are still protected by the soil from the lethal effects of temperature.

Implications: Fire implemented before seed set could be used to effectively kill a large proportion of N. trichotoma seeds. However, for more comprehensive control, it is recommended that chemical treatment is integrated with the fire treatment to improve the overall control efficiency.

Keywords: climate warming, exotic species, fire ecology, grasses, Nassella trichotoma, seed germination, serrated tussock.

Introduction

Fire is an important ecosystem disturbance in grassland communities for removing excess biomass and stimulating the regeneration of vegetation (Price et al. 2019; Yan and Liu 2021). This mechanism also correlates to improved habitat structure, which maintains important diversity regarding higher trophic levels (Price et al. 2019; Beal-Neves, et al. 2020). Fire plays a key important role in breaking seed dormancy of many grassland species, through physical scarification of seed coats (Moreira and Pausas 2012), and chemical stimulation from exposure to smoke or charcoal (Franzese and Ghermandi 2011; Nelson et al. 2012; Hodges et al. 2022). Further, fire parameters, such as heat and smoke, are known to increase germination rate and germination uniformity, which both increase the vigour of seedling emergence (Zirondi et al. 2019; Hodges et al. 2022).

Increased urban and agricultural expansion into grassland communities has resulted in the reduction of burn frequencies (Florec et al. 2020). As a consequence, the biomass of the area accumulates, leading to increased fuel loads, which often results in fire intensities that are higher than those historically recorded (Price et al. 2021). The fire regimes in many grassland communities have also been altered through the introduction and spread of invasive plants, and once established, these invasive species are able to alter the fire regimes to facilitate their dominance (Fusco et al. 2019). Consequently, if the intensity and/or frequency of fire events are altered, either the germination responses for the native species will not be activated if the intensity and frequency of fire is reduced, or they may be killed by fires that are more frequent or of higher intensity (Fusco et al. 2019; Hodges et al. 2022). Therefore, understanding how a dominant weed responds to fire events can assist in more effective management control, through the breaking of their dominance cycle and reintroducing fire regimes that represent the ecosystems historical state (Price et al. 2021).

Nassella trichotoma (Nees) Hack. ex Arechav. is considered to be one of the most economically damaging invasive plant species in Australia (Campbell and Nicol 1999), New Zealand (Bourdôt and Saville 2019) and South Africa (Joubert 1984). This species has high reproductive output, with an individual plant being able to produce over 100 000 viable seeds per year, with up to 50 000 seeds per square metre being recorded in areas with heavy infestations (Joubert 1984; Campbell and Nicol 1999). Within its native range, a significant proportion of the seeds germinate between autumn and spring, with only approximately 25% of the seeds remaining in the seedbank for longer than 1 year (Garcia et al. 2021). Within its invasive range, the seeds have been observed to persist in the soil for up to 3 years (Osmond et al. 2008); however, the majority of the seedbank is considered transient and germination will occur within the first 12 months (Ruttledge et al. 2020: Humphries and Florentine 2022). Research into developing solutions to reduce N. trichotoma’s seedbank density and longevity is therefore an important contribution for its long-term control.

One such method that merits exploration is incorporation of prescribed burning in areas invaded by N. trichotoma. Fire is an important ecosystem process that can selectively influence the recruitment of plant communities, and understanding how the seedbank of exotic plants responds to fire cues has important implications for their management (Mack et al. 2000; Franzese and Ghermandi 2011). If the required temperature to flush the seedbank or devitalise the seeds can be determined, managers can then strategically implement fire accordingly (Vermeire and Rinella 2009; Emery et al. 2011; Riveiro et al. 2019). It is noted that fire intensity is influenced by the interactions between fuel load and soil moisture, and these factors vary seasonally and across the landscape (Bradstock et al. 2010; Kreye et al. 2013).

High soil moisture often reduces the intensity of fire, whereas the intensity is significantly increased when dry matter burns (Kreye et al. 2013). Soil moisture also has a direct influence on the moisture content of seeds that lack physical dormancy structures (Tangney et al. 2018). Physiological processes within the seed become more active with increasing seed moisture levels (Walters et al. 2005) and, subsequently, seeds become more susceptible to devitalisation when exposed to high temperatures (Tangney et al. 2018). It has been observed that high seed moisture conditions can reduce the seed’s ability to resist fire, demonstrating that lower-intensity burns can still provide effective control of invasive plants (Fer and Parker 2005). Therefore, understanding the interactions of seed moisture levels and fire intensity can be important for knowing when to implement strategic burns in weed-dominant areas.

It is known that seedling recruitment increases in volume and uniformity when N. trichotoma is exposed to fire (Joubert 1984; Hamilton 2012). Fire has also been observed to destroy approximately 18% of this species’ seedbank (Wells and De Beer 1987). Another adaptive trait seen in fire-prone ecosystems is the ability for established plants to re-shoot rapidly after a fire event (Pausas and Keeley 2014). This trait has been observed in N. trichotoma, which is a result of the plant’s base being well protected by its dense tussock growth form (Osmond et al. 2008). Once established, this weed alters fire regimes for its self-facilitation by producing higher than historic fuel loads through slow nutrient cycling and grazing avoidance (Moretto and Distel 2002). Because higher than historic fuel loads negatively affect native seeds and plants during fire events, fire has not been recommended for N. trichotoma control programs, despite it successfully flushing the persistent surface seedbank (Osmond et al. 2008).

The objective of this paper is to identify the response of N. trichotoma seeds of different (1) ages and (2) moisture content levels to an increased time of exposure to radiant heat. The ability of established plants to recover from these factors will also be explored. The findings of this research will provide important information leading to a better understanding of how N. trichotoma responds to fire and, consequently, what fire regimes might be useful in particular circumstances.

Materials and methods

Seed collection and preparation

Seeds were collected from mature N. trichotoma plants in Mambourin, Victoria, Australia (37°55′18.12″S, 144°32′43.079″E), located within the Greater Western Grasslands in central Victoria, Australia (Fig. 1), in December 2016, 2017, 2018 and 2019. The seeds were stored within their panicles in zip-locked bags at room temperature until use. When the study was about to commence, seeds were removed from the panicles and gently squeezed with forceps to test for seed fill. Seeds that collapsed easily were discarded. Seed mass was determined for each age class by weighing 100 randomly selected seeds from each age group.

Fig. 1. 

Map showing seed-collection areas located within the Greater Western Grasslands in central Victoria, Australia.


BT22078_F1.gif

Effect of radiant heat on seed germinability

For each treatment combination, 25 seeds were counted and placed into aluminium bowls (10 cm in diameter), and were then exposed to temperatures of either 80°C, 100°C, 120°C or 140°C for 1, 3, 6 or 9 min inside a temperature-controlled oven (Memmert, Type No. ULE500). This multifactor experiment contained four seed ages, four heat treatments and four exposure durations for a total of 64 treatment combinations, plus a control for each seed-collection year. Each treatment combination was replicated six times.

Immediately following heat exposure, seeds were placed into Petri dishes lined with sterilised filter paper and moistened with sterilised reverse osmosis (RO) water, with parafilm being used to prevent drying. The treatments were placed into incubation chambers set to alternating 25°C/15°C, 12-h light/12-h dark conditions, which have been pre-determined as the optimal growth conditions for N. trichotoma (Humphries et al. 2018). The treatments were checked twice a week for 35 days and germination was determined by protrusion of the radicle.

Effect of moisture content and radiant heat on seed germinability

It was observed that the seed collected in 2016 provided the highest germination across all tested temperatures, and they were therefore preferentially selected for the rehydration treatments. To prepare for the experiments, nylon mesh bags containing filled seeds (determined by the squeeze test described previously) were secured within an airtight polycarbonate electrical enclosure box (28 × 28 × 14 cm) containing LiCl solutions adjusted to either 15% RH (740 g/L), 50% RH (364 g/L), or 95% RH (48 g/L). The relative humidity (RH) levels were selected because these moisture contents are associated with the three distinct seed hydration levels that have previously been shown to promote different physiological activity within the seeds (Walters et al. 2005). The boxes were stored at 20°C for 2 weeks, and seed hydration was assessed at the end of this period with a digital hygrometer. After the rehydration period, the seeds were exposed to the methods previously described for heat exposure and subsequent germination monitoring.

Effect of radiant heat on established plants

To assess the effect of radiant heat on established plants, 100 plastic garden pots (140 mm in diameter and 140 mm in height) were lined with absorbent towelling, filled with a fine layer of river sand and then topped with commercially purchased soil. Five viable N. trichotoma seeds were placed into each pot and lightly covered with soil. The pots were placed into watertight plastic trays (28 cm × 44 cm × 5.5 cm), and were placed into a glasshouse at ambient temperature on 24 February 2022. Pots were bottom-watered at least once a week and seedlings were thinned to one plant per pot after the first month of growth. The final plants were grown under glasshouse conditions for 3 months.

The heat treatments were conducted on 22 May 2022. To prepare the plants for the heat-exposure experiment, the plant and soil were together carefully removed from the pots and placed into heat-safe aluminium trays. Five plants were randomly selected and exposed to radiant heat levels of 20°C, 60°C, 80°C, 100°C or 120°C for 3, 6 or 9 min. The plants were then re-potted and monitored for a further 2 weeks under glasshouse conditions, when any signs of wilting or recovery were visually observed.

Data analysis

Effect of radiant heat on seed germinability

To determine whether the collection year, the temperature or the duration of exposure had a significant influence on total germination, the data were tested using a three-way ANOVA by using the statistical analysis program SPSS (IBM). This test accounted for all possible interactions of these factors, and the significance was set to 0.05.

The total germination percentage, the mean germination time (MGT), germination index (GI) and time to 50% germination (T50), were calculated using the following formulae:

1. Mean germination time was calculated using the equation

Mean germination time =ΣDn/Σn

where n is the number of seeds, which were germinated on Day Dn, and n is the number of days counted from the beginning of germination (Sadeghi et al. 2011).

2. The germination index was calculated as described in the Association of Official Seed Analysis (AOSA 1993) by following the formula:

No. of germinated seeds/day of first count ++  No. of germinated seeds/day of final count

3. The time to reach 50% germination was calculated using the formula as described by Kader (2005), as follows:

Time taken to reach 50% germination (T50)=ti( n2 ni )( tj ti )njni

where n is the final number of germinated seeds, and nj and ni are the cumulative number of seeds germinated by adjacent counts at Times tj (day) and ti (day) respectively, when ni < n/2 < nj.

Effect of moisture content and radiant heat on seed germinability

The germination totals were tested for significant interactions by using a three-way ANOVA, by using the statistical analysis program SPSS (IBM®) to determine the effects of hydration level, temperature, duration of exposure and all possible interactions of these factors.

Effect of radiant heat on established plants

A mean damage score was calculated for each experiment to assess the condition of the plants. The damage scores were determined as follows: (1) 0 = no damage, (2) 1 = some dryness observed on only the tips of the leaves, or (3) 2 = extensive drying observed to the leaves.

Results

Climate conditions for each collection year

Variations in the seed mass were observed among the collections made across the different years, with the highest seed mass being recorded for the seeds collected in 2016, which correlated with optimal germination parameters (Table 1). In 2016, the average spring maximum monthly temperature was lower than in the following years, and the total rainfall was much higher during the same period, and these factors may have contributed to the higher seed mass than for the seeds collected in 2017–2019. The higher average spring temperature may have been a leading cause for the reduced seed mass for those collected in 2017, whereas the low total spring rainfall may have contributed to the low seed mass in the seeds collected in 2019.

Table 1. The total rainfall (mm) and average maximum temperatures (°C) for the spring months (September–November) during 2016–2019, together with the seed mass observed for each collection.

Collection yearSpring rainfall (mm)Average spring temperature (°C)Seed mass (g)
2016178.8190.0709
201795.221.70.0429
20187620.90.0641
201943.720.40.0481

Note: data were sourced from Mount Rothwell weather station, which is located approximately 10 km from the seed-collection site (Bureau of Meteorology 2021).

Effect of radiant heat on seed germinability

The effect of temperature (P < 0.001), duration of exposure (P < 0.001), and seed-collection year (P < 0.001) had a significant impact on N. trichotoma’s total seed germination (%), as did the interactions of these factors (Table 2). The control experiment (no heat) demonstrated that seeds collected in 2016 had a significantly higher total germination percentage than did the seeds collected in more recent years, and the germinability of the seeds appeared to increase with the age of collection, with the total germination percentage increasing with the age of the seeds (Table 3).

Table 2. The effect of increased radiant-heat exposure on the germination of N. trichotoma seeds of increasing age.

Factord.f.FP-value
Population365.41<0.001
Temperature3395.12<0.001
Time36.49<0.001
Population × temperature917.27<0.001
Population × time92.580.007
Temperature × time93.91<0.001

Significance was set to 0.05.

d.f., degrees of freedom.

Table 3. Germination percentage (Ger %), germination index (GI), mean germination time (MGT), and time to 50% germination (T50) after increased exposure to radiant heat for four populations of N. trichotoma seeds.

PopulationTemperature (°C)Time (min)Ger (%)GIMGTT50
2016Control091.332.749.187.62
8011003.507.366.52
394.673.207.616.60
674.672.389.826.76
998.673.268.066.62
10011003.088.807.58
398.672.3311.8611.19
699.332.6110.7410.03
999.332.3211.5711.43
120184.001.3317.0616.29
384.001.3218.4817.19
686.001.4815.1413.63
986.671.2818.4714.75
2017Control078.672.0511.847.78
80178.672.329.317.91
378.001.1512.8510.64
646.002.3110.289.16
985.331.9110.768.01
100168.002.069.948.89
368.001.209.477.79
639.330.8616.169.52
931.330.7616.1614.08
120134.001.2317.7816.33
382.000.9218.7517.49
666.671.2816.8016.13
980.670.7719.6317.71
2018Control075.331.2817.0313.37
80159.331.1514.6213.88
368.001.4913.389.78
650.670.8816.8413.97
972.001.5513.9912.49
100168.671.3215.3514.48
380.671.6813.8813.48
666.001.3915.1512.52
975.331.3516.6613.65
120174.001.1218.1916.64
330.670.3820.8619.50
640.000.4422.2721.86
958.670.6224.0022.19
2019Control053.331.0914.9713.01
80162.671.2313.7911.64
342.670.5819.4017.24
616.670.2122.1420.55
965.331.2214.6612.65
100144.000.4825.0522.68
362.000.9919.5517.94
664.001.2814.4211.85
970.001.4016.4013.01
120168.000.8521.1218.42
334.670.3527.7927.63
638.000.4525.2021.69
98.000.07034.50

Note: the 140°C treatment was not included in this Table as germination was insufficient to conduct analysis.

Total germination percentage and GI decreased as the temperature gradient increased, whereas the effect of the duration of the heat exposure had a lesser effect on these factors (Table 2). A similar observation was made for mean germination time (MGT) and time to 50% germination (T50), with these parameters increasing when exposed to the higher temperature gradients. The two older seed collections, namely from 2016 and 2017, reached 50% germination sooner than the more recently collected seeds in 2018 and 2019. In most cases, the heat treatments increased N. trichotoma germination percentage compared with the germination percentage recorded for the control treatment. For all the seed-collection times, the 140°C temperature was significant at reducing total seed germination percentage, with the exception of only 0.64% of the seeds germinating in the 6- and 9-min treatments for the seeds collected in 2018. The seeds collected in 2019 had significantly reduced viability when exposed to 120°C for 9 min; however, this decline was not observed for the other treatments. There are variations in total germination percentage for the 80°C, 100°C and 120°C treatments for all the collected seeds, with 2016 having the highest consistency.

Effect of moisture content and radiant heat on seed germinability

As the seeds collected in 2016 provided the highest total germination percentage under controlled testing, as well as providing the most uniformed germination percentage across all temperatures, these seeds were selected for the subsequent tests.

The seed moisture content (P < 0.001), temperature (P = 0.002), and their interaction (P < 0.001) were significant factors affecting N. trichotoma total seed germination percentage (Table 4). Seeds hydrated to 15% had no significant difference in germination percentage when exposed to 80°C, 100°C or 120°C, and the first two temperatures increased germination percentage when compared with the control (Table 5). The seeds hydrated to 50% experienced a significant decline in total germination percentage when the seeds were exposed to 120°C for 9 min (P = 0.002). The exposure to heat was lethal to seeds with moisture contents of 90%, with only 4.6% of the seeds germinating after 1 min of exposure to 80°C. No further germination occurred for seeds hydrated to 90%.

Table 4. The effect of increased radiant-heat exposure on the germination of N. trichotoma seeds rehydrated to 15%, 50% and 95%.

Factord.f.FP-value
Seed hydration25463.92<0.001
Temperature26.590.002
Time30.380.761
Seed hydration × temperature411.52<0.001
RH% × time60.650.687
Temperature × time60.210.975
Seed hydration × temperature × time120.830.614

Significance was set to 0.05.

d.f., degrees of freedom.

Table 5. The germination response of hydrated N. trichotoma seeds to radiant heat.

HydrationTemperature (°C)Duration (min)
1369
15%8090.66969694
10099.3310098.6697.33
12097.3390.6690.6690.66
50%801009690.6698
10099.3394.669698.66
1208888.6688.6681.33
95%804.6000
1000000
1200000

Note: the seeds were hydrated to either 15%, 50%, or 95% and then exposed to one of three temperatures, namely 80°C, 100°C, and 120°C, for 1, 3 6, or 9 min. The control treatment of no heat or hydration pre-treatment and recorded 91.33% total germination.

Effect of radiant heat on seedlings

All the plants exposed to the temperatures of 20°C and 60°C were undamaged, and the leaves remained a vibrant green from the base to the tip. At the higher temperatures tested, namely 80°C, 100°C, and 120°C, notable drying of the leaves was observed, but the base of the plant remained undamaged. Four plants exposed to the 120°C treatment (two exposed for 6 min, and two exposed for 9 min) suffered extensive drying, but these plants resprouted from the base. Fig. 2 shows the visual differences among the damage scores of 1 (undamaged), 2 (leaf drying) and 3 (extensive leaf drying and resprouting). No plants were completely killed from the trialled heat treatments.

Fig. 2. 

(L → R) Visual differences among the damage scores of 1 (undamaged), 2 (leaf drying) and 3 (extensive leaf drying and resprouting).


BT22078_F2.gif

Discussion

Seed germinability

Our results observed a significant increase in germination percentage for the seeds collected in 2016 compared with those from the following collection years, with the most recent seeds, namely those collected in 2019, demonstrating the lowest germination percentage. In many cases, seed viability and seedling vigour decline as time in dry storage increases (De Vitis et al. 2020), making the results of the present study controversial. Studies into N. tricotoma’s seed longevity under field conditions suggest that the majority of this species seedbank will germinate within the first year of seed set, with only small proportion (<10%) demonstrating short-term persistence of up to 3 years (Ruttledge et al. 2020; Humphries and Florentine 2022). However, under stored conditions, 20-year-old seeds of this species have been observed to germinate successfully (Taylor 1987). This suggests that dry storage does not have a significant impact on N. trichotoma seed viability.

The complex interactions of various biotic and abiotic pressures experienced by the maternal environment during seed development can result in interannual variations in seed traits (Franzese and Ghermandi 2011; Pearse et al. 2017). Various environmental factors, such as temperature and rainfall that a plant experiences during its seed-development stage, can directly influence the progeny seeds dormancy and germination potential (Penfield and MacGregor 2017; Souza et al. 2019). For example, the combination of high temperature and osmotic stress reduce the production of viable seeds of the invasive annual grass Avena fatua (Peters 1982). Plants exposed to higher rainfall and soil nutrients will often allocate more resources to reproduction, resulting in higher seed output and seeds of greater mass and size (Salisbury 1943; Lazaro-Nogal et al. 2015; Souza et al. 2019). The substantially higher spring rainfall experienced in 2016 than that in the following years, may have been one of the factors contributing to the higher seed mass observed for this collection year. Increased seed mass can often result in more vigorous germination and seedling emergence, providing these seeds with a competitive advantage in this critical life stage (Vaughton and Ramsey 2001; Paz and Martinez-Ramos 2003).

The seeds collected in 2016 had greater average seed mass than did those collected in the subsequent years, which was a significant issue for the investigation because increased seed mass can improve the total germination percentage and germination time, together with improving the success of the seedling survival (Bonfil 1998; Cordazzo 2002). The results of this study support the contention that greater seed mass increases total gemination percentage and germination time compared with seeds with a reduced mass. Additionally, an inverse relationship in seed size and seed longevity has been observed for several grassland species, including Ambrosia trifida (Schutte et al. 2008), whereby the smaller seeds persist longer in the seedbank than do larger, denser seeds. It is possible that N. trichotoma has adopted a similar strategy in the present study, and the lighter seeds collected in 2019 may have a higher proportion of dormant seeds, therefore reducing the germinability of this sample.

Understanding the variations in the degree of dormancy a population displays has important implications on the populations ability to successfully establish and persist (Baloch et al. 2001). It is known that N. trichotoma experiences a primary dormancy period that extends for approximately 3 months, which prevents the seeds from germinating in the water-limited summer months (Osmond et al. 2008). This species has also demonstrated the capacity to undergo secondary dormancy, which is induced when the seeds are exposed to prolonged unfavourable conditions, even after the primary dormancy period has ended (Buijs 2020). Intraspecific variations in secondary dormancy are important for ensuring survival in disturbance-prone ecosystems, such as the grassland communities that N. trichotoma has successfully invaded, because this strategy protects the population from failed establishment in times where multiple disturbances are present, such as multiple fire events or prolonged drought (Liyanage and Ooi 2015).

Effect of radiant heat on seed age

N. trichotoma seeds demonstrated a high level of resistance to the tested radiant-heat treatments, with seeds collected in 3 of the 4 years maintaining a high total germination percentage at 120°C. The only exception was seen in the seeds collected in 2019, where the seed germination was significantly (P = 0.002) reduced when exposed for 9 min at 120°C treatment. For the seeds collected in 2016, exposure to 80°C and 100°C increased the total germination percentage compared with the control. The seeds collected in 2017–2019 also evidenced an increased total germination percentage compared with the control.

Mean germination time indicates the lag period between seed imbibition and radicle protrusion where the seed undergoes repairs from damages caused by the environment or seed aging (Mavi et al. 2010). In the present study, N. trichotoma seeds decreased their mean germination time (MGT) after exposure to the increasing temperature gradient, particularly when the exposure time was short. Longer duration of exposure to the temperature gradient resulted in an increase in MGT, indicating these seeds required time to repair any damage prior to germination.

The ability of a species to germinate with greater speed and uniformity increases its competitiveness following fire (Hodges et al. 2022). Mean germination time can be used as an indicator in determining field emergence, with an increased MGT being correlated to lower and less vigorous field emergence (Matthews and Khajeh-Hosseini 2006). Although this could indicate that a high-intensity fire that heats the soil to 120°C or above could damage the seeds enough to reduce competitive emergence in field, this would, however, be subject to the parallel fire response of the native species in the same corresponding seedbank area (Hodges et al. 2022). Time to 50% germination followed the same pattern as did MGT, whereby germination rate slowed as the temperature gradients and duration of exposure increased.

The 140°C treatment was shown to significantly devitalise the seeds, with the exception of one seed germinating in each of the 6- and 9-min-exposure treatments (0.64%) for the seeds collected in 2018. This temperature has been observed to be lethal in other awned grass seeds, such as Piptochaetium napostaense (Kin et al. 2016). Seed awns are an important adaptive trait for seed survival in fire-prone ecosystems, and increased fire intensity can be a selection mechanism for awns with an increased length, because this allows for the seed to burrow further into the soil to escape lethal temperatures (Garnier and Dajoz 2001). The hygroscopic awn on N. trichotoma seeds allows it to burrow into the soil profile, with the majority of this species seedbank found buried at an approximately 2.5-cm depth (Joubert 1984). Shallow seed burial can alleviate the severity of heat shock from fire events, and temperatures 2 cm below the soil surface rarely exceed 80°C (Penman and Towerton 2008). Indeed, a controlled study demonstrated that for surface temperatures that reached 500°C, these conditions were reduced to approximately 70°C at 2 cm depth (Girona-Garcia et al. 2015). Another study showed a significant reduction in temperature (approximately 60%) at a depth of 1 cm, and increased soil moisture further reduced the transfer of heat into the soil profile (Valette et al. 1994). It is therefore unlikely that the majority of N. trichotoma seeds that have burrowed into the soil will be exposed to temperatures that exceed their lethal temperature threshold.

Effect of radiant heat on hydrated seeds

The moisture levels of vegetation and the soil have been shown to influence the intensity of prescribed fire, with the highest-intensity fires thus occuring under low moisture levels. Soils with a high moisture content decrease the thermal energy of the fire (Valette et al. 1994), and this is due to (1) a reduced rate of fuel consumption (Marino et al. 2012), and (2) water in the soil dissipating heat as steam (Stoof et al. 2013). The soil moisture levels strongly influence the moisture level of the seeds that reside within the subsequent soil seedbank, particularly those lacking physical dormancy structures (Dasberg 1971; Josuah et al. 1994). However, N. trichtoma seeds possess no such structures, but and can readily take up water when it is available in the soil (Campbell and Nicol 1999).

Germination percentages for the seeds hydrated to 15% and 50% experienced no significant changes in germination compared with the control treatment. The seeds hydrated to 95% experienced a significant decline in germination percentage at all tested temperatures. The literature suggests that seeds hydrated to 95% are killed by much lower temperatures than those with lower moisture contents (Ruprecht et al. 2016; Tangney et al. 2018), and in the present study, this was confirmed by comparison with levels of 15% and 50%. As the seed moisture content increases, so too does the seeds physiological activity (Walters et al. 2005). When the seeds are hydrated above 90%, there is high free-water content within the seeds, and this can be heated to a temperature that damages cellular processes, subsequently stopping the physiological processes that initiate the germination process (Tangney et al. 2018). Also, proteins associated with protecting the seed while it is in a dormant state, including the synthesis of small heat-shock proteins, cease to provide adequate protection at high seed moisture levels as they do when the seed is in a dry and dormant state (Wehmeyer et al. 1996).

Effect of radiant heat on seedlings

It has been reported that prescribed burning has been implemented effectively for weed-control programs and ecological restoration of grasslands (Mainardis et al. 2020; Assis et al. 2021). However, it is known that adult N. trichotoma plants are able to resist high-intensity fire (Joubert 1984; CRC 2003), and our results suggested that this resistance is also demonstrated in 3-month-old seedlings. In our work, the N. trichotoma seedlings resisted all the temperatures and duration of exposure times tested in this study, and no plants were killed up to 2 weeks post-heat exposure. Exposure to the 120°C treatment did cause extensive drying to the leaves; however, in some cases, the plant was seen to resprout from the base. The ability to resprout rapidly following a fire is critical for maintaining competitive dominance, and ensuring survival of the population, particularly when the seedbank may have been depleted following a fire through either increased seed germination or devitalisation (Tangney et al. 2020; Hodges et al. 2022).

This study has thus demonstrated that N. trichotoma can withstand high temperatures related to fire. Because this species produces unpalatable, sclerophyllous leaves, it allows it to contribute a large volume of dry biomass to the grasslands that it invades (Distel 2013). This further allows for this species to contribute to increases in the intensity of fire regimes, which it can withstand, and thus successfully displace native plants, which cannot survive such high temperatures. This suggests that for control of N. trichotoma, it would be recommended that managers use fire-integrated techniques, using control actions such as target spraying this species with herbicide prior to burning, then broadcasting competing seeds and introducing controlled grazing post-fire (Distel 2013) in grassland ecosystems.

Conclusions

In this paper, we explored the response of N. trchotoma seeds and seedlings to fire through controlled radiant heat-exposure trials. Whereas the seeds were able to survive temperatures of 120°C, the majority of the seeds were killed when exposed to 140°C. This suggests that only seeds at the soil surface, or within the top 1 cm, could be killed by hot fire, because these temperatures are alleviated by the soil, producing favourable temperatures for spiking germination (approximately 80°C) below this depth. Both MGT and T50 increased under higher temperature gradients and duration of exposure, suggesting that these treatments caused intracellular damage, whereas the delayed germination was due to the seeds requiring time to repair. The seed mass for each collection year appeared to be a key indicator of germinability, with higher seed mass producing the highest germination percentage. Implementing fire with increased moisture levels may not be effective for managing this species, because no change in germination percentage was observed for seeds pre-treated to 50% hydration. Almost all the seeds were killed when hydrated to 95%; however, achieving effective heat penetration into the soil profile at this soil moisture level poses its own challenges. Last, whereas no seedlings were killed by the applied treatments, the 120°C treatment did result in extensive drying to the leaves, causing resprouting from the base of the plant.

Rapid seedling recruitment from the seedbank has been observed for N. trichotoma following fire events, and the results of the present study suggested that a moderate-heat fire will reduce the time to 50% germination, which supports observations in the field. For fire to be used effectively to kill N. trichotoma, it should be implemented in conjunction with other control actions.

Data availability

The data that support this study will be shared upon reasonable request to the corresponding author.

Conflicts of interest

The authors declare that there are no conflicts of interest.

Declaration of funding

This research was supported by an Australian Government Research Training Program (RTP) Stipend and RTP Fee-Offset Scholarship through Federation University Australia.

References

AOSA (1993Available at) Rules for testing seeds. Journal of Seed Technology 16, 1-113 https://www.jstor.org/stable/23432704.
| Google Scholar |

Assis GB, Pilon NAL, Siqueira MF, Durigan G (2021) Effectiveness and costs of invasive species control using different techniques to restore cerrado grasslands. Restoration Ecology 29, e13219.
| Crossref | Google Scholar |

Baloch HA, Di Tommaso A, Watson AK (2001) Intrapopulation variation in Abutilon theophrasti seed mass and its relationship to seed germinability. Seed Science Research 11, 335-343.
| Google Scholar |

Beal-Neves M, Chiarani E, Ferreira PMA, Fontana CS (2020) The role of fire disturbance on habitat structure and bird communities in South Brazilian Highland Grasslands. Scientific Reports 10, 19708.
| Crossref | Google Scholar |

Bonfil C (1998) The effects of seed size, cotyledon reserves, and herbivory on seedling survival and growth in Quercus rugosa and Q. laurina (Fagaceae). American Journal of Botany 85, 79-87.
| Crossref | Google Scholar |

Bourdôt GW, Saville DJ (2019) Nassella trichotoma – plant growth rates and effects of timing of grubbing on populations in North Canterbury grassland. New Zealand Journal of Agricultural Research 62, 224-245.
| Crossref | Google Scholar |

Bradstock RA, Hammill KA, Collins L, Price O (2010) Effects of weather, fuel and terrain on fire severity in topographically diverse landscapes of south-eastern Australia. Landscape Ecology 25, 607-619.
| Crossref | Google Scholar |

Buijs G (2020) A perspective on secondary seed dormancy in Arabidopsis thaliana. Plants 9, 749.
| Crossref | Google Scholar |

Bureau of Meteorology (2021) Climate data online. Australian Government. Available at http://www.bom.gov.au/climate/data/ [Accessed 7 July 2022]

Campbell MH, Nicol HI (1999) Seed dormancy in Serrated tussock (Nassella trichotoma (Nees) Arech.) in New South Wales. Plant Protection Quarterly 14, 82-85.
| Crossref | Google Scholar |

Cordazzo CV (2002) Effect of seed mass on germination and growth in three dominant species in southern Brazilian coastal dunes. Brazilian Journal of Biology 62, 427-435.
| Crossref | Google Scholar |

CRC (2003) Weed management guide; serrated tussock (Nassella trichotoma). pp. 1–6.

Dasberg S (1971) Soil water movement to germinating seeds. Journal of Experimental Botany 22, 999-1008.
| Crossref | Google Scholar |

De Vitis M, Hay FR, Dickie JB, Trivedi C, Choi J, Fiegener R (2020) Seed storage: maintaining seed viability and vigor for restoration use. Restoration Ecology 28, S249-S255.
| Crossref | Google Scholar |

Distel RA (2013) Unpalatable perennial grass invasion in central-east Argentina native grasslands: processes, implications and recovery. In ‘Control and management of weeds and diseases of grass and forage systems. Proceedings of the 22nd international grassland congress, 15–19 September 2013, Sydney, NSW, Australia’.

Emery SM, Uwimbabazi J, Flory SL (2011) Fire intensity effects on seed germination of native and invasive Eastern deciduous forest understory plants. Forest Ecology and Management 261, 1401-1408.
| Crossref | Google Scholar |

Fer DL, Parker VT (2005) The effect of seasonality of burn on seed germination in chaparral: the role of soil moisture. Madroño 52, 166-174.
| Crossref | Google Scholar |

Florec V, Burton M, Pannell D, Kelso J, Milne G (2020) Where to prescribe burn: the costs and benefits of prescribed burning close to houses. International Journal of Wildland Fire 29, 440-458.
| Crossref | Google Scholar |

Franzese J, Ghermandi L (2011) Seed longevity and fire: germination responses of an exotic perennial herb in NW Patagonian grasslands (Argentina). Plant Biology 13, 865-871.
| Crossref | Google Scholar |

Fusco EJ, Finn JT, Balch JK, Nagy RC, Bradley BA (2019) Invasive grasses increase fire occurrence and frequency across US ecoregions. Proceedings of the National Academy of Sciences 116, 23594-23599.
| Crossref | Google Scholar |

Garcia A, Loydi A, Distel RA (2021) Temporal and spatial variation in the soil seed bank of Nassella trichotoma (serrated tussock) in its native range. Australian Journal of Botany 69, 45-51.
| Crossref | Google Scholar |

Garnier LKM, Dajoz I (2001) Evolutionary significance of awn length variation in a clonal grass of fire-prone savannas. Ecology 82, 1720-1733.
| Crossref | Google Scholar |

Girona-Garcia A, Badia-Villas D, Marti-Dalmau C, Arjona-Garcia B (2015) Soil depth affected by fire: a laboratory approach to measure temperature variations. In ‘5th international conference of fire effects on soil properties, Dublin, 14–17 July 2015’. The Northwest Fire Science Consortium. Available at https://www.researchgate.net/publication/292551300_Soil_depth_affected_by_fire_a_laboratory_approach_to_measure_temperature_variations

Hamilton C (2012) Serrated tussock. Victorian Serrated Tussock Working Party. Available at http://www.serratedtussock.com.au/

Hodges JA, Price JN, Nicotra AB, Guja LK (2022) Smoke and heat can increase germination of common wildflowers and grasses – implications for conservation and restoration of critically endangered grassy ecosystems. Ecological Management & Restoration 23, 94-99.
| Crossref | Google Scholar |

Humphries T, Florentine S (2022) Assessing seedbank longevity and seed persistence of the invasive tussock grass Nassella trichotoma using in-field burial and laboratory-controlled ageing. Plants 11, 2377.
| Crossref | Google Scholar |

Humphries T, Chauhan BS, Florentine SK (2018) Environmental factors effecting the germination and seedling emergence of two populations of an aggressive agricultural weed; Nassella trichotoma. PLoS ONE 13, e0199491.
| Crossref | Google Scholar |

Josuah M, Favier J, Yule I (1994Available at) Model of moisture uptake by wheat seeds germinating in free water. International Agrophysics 8, 251-257 http://www.international-agrophysics.org/Model-of-moisture-uptake-by-wheat-seeds-germinating-in-free-water,139704,0,2.html.
| Google Scholar |

Joubert DC (1984) The soil seed bank under Nasella tussock infestations at Boschberg. South African Journal of Plant and Soil 1, 1-3.
| Crossref | Google Scholar |

Kader MA (2005Available at) A comparison of seed germination calculation formulae and associated interpretation of resulting data. Journal and Proceedings of the Royal Society of New South Wales 138, 65-75 https://www.semanticscholar.org/paper/A-Comparison-of-Seed-Germination-Calculation-and-of/cbb8ac13a5a6de85cb84b3f7093623aec7ae9b02.
| Google Scholar |

Kin AG, Suarez CE, Chirino CC, Avila PL, Morici EFA (2016) Impact of heat on seed germination of three perennial grasses in the semiarid region in Central Argentina. Australian Journal of Botany 64, 451-455.
| Crossref | Google Scholar |

Kreye JK, Kobziar LN, Zipperer WC (2013) Effects of fuel load and moisture content on fire behaviour and heating in masticated litter-dominated fuels. International Journal of Wildland Fire 22, 440-445.
| Crossref | Google Scholar |

Lazaro-Nogal A, Matesanz S, Godoy A, Perez-Trautman F, Gianoli E, Valladares F (2015) Environmental heterogeneity leads to higher plasticity in dry-edge populations of a semi-arid Chilean shrub: insights into climate change responses. Journal of Ecology 103, 338-350.
| Crossref | Google Scholar |

Liyanage GS, Ooi MKJ (2015) Intra-population level variation in thresholds for physical dormancy-breaking temperature. Annals of Botany 116, 123-131.
| Crossref | Google Scholar |

Mack RN, Simberloff D, Mark Lonsdale W, Evans H, Clout M, Bazzaz FA (2000) Biotic invasions: causes, epidemiology, global consequences, and control. Ecological Applications 10, 689-710.
| Crossref | Google Scholar |

Mainardis M, Boscutti F, Rubio Cebolla MdM, Pergher G (2020) Comparison between flaming, mowing and tillage weed control in the vineyard: effects on plant community, diversity and abundance. PLoS ONE 15, e0238396.
| Crossref | Google Scholar |

Marino E, Dupuy JI, Pimont F, Guijaro M, Hernando C, Linn RR (2012) Fuel bulk density and fuel moisture content effects on fire rate of spread: A comparison between FIRETEC model predictions and experimental results in shrub fuels. Journal of Fire Science 30, 277-299.
| Google Scholar |

Matthews S, Khajeh-Hosseini M (2006) Mean germination time as an indicator of emergence performance in soil of seed lots of maize (Zea mays). Seed Science and Technology 34, 339-347.
| Crossref | Google Scholar |

Mavi K, Demir I, Matthews S (2010) Mean germination time estimates the relative emergence of seed lots of three cucurbit crops under stress conditions. Seed Science and Technology 38, 14-25.
| Crossref | Google Scholar |

Moreira B, Pausas JG (2012) Tanned or burned: the role of fire in shaping physical seed dormancy. PLoS ONE 7, e51523.
| Crossref | Google Scholar |

Moretto AS, Distel RA (2002) Soil nitrogen availability under grasses of different palatability in a temperate semi-arid rangeland of central Argentina. Austral Ecology 27, 509-514.
| Crossref | Google Scholar |

Nelson DC, Flematti GR, Ghisalberti EL, Dixon KW, Smith SM (2012) Regulation of seed germination and seedling growth by chemical signals from burning vegetation. Annual Review of Plant Biology 63, 107-130.
| Crossref | Google Scholar |

Osmond R, Verbeek M, McLaren DA, Michel-More M, Wicks B, Grech CJ, et al. (2008) Serrated tussock-national best practice manual. Available at http://serratedtussock.com/wp-content/uploads/files/Serrated-Tussock-National-Best-Practice-Management-Manual.pdf

Pausas JG, Keeley JE (2014) Evolutionary ecology of resprouting and seeding in fire-prone ecosystems. New Phytologist 204, 55-65.
| Crossref | Google Scholar |

Paz H, Martinez-Ramos M (2003) Seed mass and seedling performance within eight species of Psychotria (Rubiaceae). Ecology 84, 439-450.
| Crossref | Google Scholar |

Pearse IS, LaMontagne JM, Koenig WD (2017) Inter-annual variation in seed production has increased over time (1900–2014). Proceedings of the Royal Society B: Biological Sciences 284, 20171666.
| Crossref | Google Scholar |

Penfield S, MacGregor DR (2017) Effects of environmental variation during seed production on seed dormancy and germination. Journal of Experimental Botany 68, 819-825.
| Crossref | Google Scholar |

Penman TD, Towerton AL (2008) Soil temperatures during autumn prescribed burning: implications for the germination of fire responsive species? International Journal of Wildland Fire 17, 572-578.
| Crossref | Google Scholar |

Peters NCB (1982) The dormancy of wild oat seed (Avena fatua L.) from plants grown under various temperature and soil moisture conditions. Weed Research 22, 205-212.
| Crossref | Google Scholar |

Price JN, Good MK, Schultz NL, Guja LK, Morgan JW (2019) Multivariate drivers of diversity in temperate Australian native grasslands. Australian Journal of Botany 67, 367-380.
| Crossref | Google Scholar |

Price JN, Schultz NL, Hodges JA, Cleland MA, Morgan JW (2021) Land-use legacies limit the effectiveness of switches in disturbance type to restore endangered grasslands. Restoration Ecology 29, e13271.
| Crossref | Google Scholar |

Riveiro SF, Garcia-Duro J, Cruz O, Casal M, Reyes O (2019) Fire effects on germination response of the native species Daucus carota and the invasive alien species Helichrysum foetidum and Oenothera glazioviana. Global Ecology and Conservation 20, e00730.
| Crossref | Google Scholar |

Ruprecht E, Lukács K, Domokos P, Kuhn T, Fenesi A (2016) Hydration status influences seed fire tolerance in temperate European herbaceous species. Plant Biology 18, 295-300.
| Crossref | Google Scholar |

Ruttledge A, Whalley RDB, Falzon G, Backhouse D, Sindel BM (2020) The role of soil temperature and seed dormancy in the creation and maintenance of persistent seed banks of Nassella trichotoma (serrated tussock) on the Northern Tablelands of New South Wales. The Rangeland Journal 42, 85-95.
| Crossref | Google Scholar |

Sadeghi H, Khazaei F, Yari L, Sheidaei S (2011Available at) Effect of seed osmopriming on seed germination behavior and vigor of soybean (Glycine max L.). Journal of Agricultural and Biological Science 6, 39-43 https://www.researchgate.net/publication/265893247_Effect_of_seed_osmopriming_on_seed_germination_behavior_and_vigor_of_soybean_Glycine_max_L.
| Google Scholar |

Salisbury EJ (1943) ‘The reproductive capacity of plants.’ (Bell and Sons: London, UK). Available at https://www.nature.com/articles/151319a0

Schutte BJ, Regnier EE, Harrison SK (2008) The association between seed size and seed longevity among maternal families in Ambrosia trifida L. populations. Seed Science Research 18, 201-211.
| Crossref | Google Scholar |

Souza ML, Lovato MB, Fagundes M, Valladares F, Lemos-Filho JP (2019) Soil fertility and rainfall during specific phenological phases affect seed trait variation in a widely distributed Neotropical tree, Copaifera langsdorffii. American Journal of Botany 106, 1096-1105.
| Crossref | Google Scholar |

Stoof CR, Moore D, Fernandes PM, Stoorvogel JJ, Fernandes RES, Ferreira AJD, Ritsema CJ (2013) Hot fire, cool soil. Geophysical Research Letters 40, 1534-1539.
| Crossref | Google Scholar |

Tangney R, Merritt DJ, Fontaine JB, Miller BP (2018) Seed moisture content as a primary trait regulating the lethal temperature thresholds of seeds. Journal of Ecology 107, 1093-1105.
| Crossref | Google Scholar |

Tangney R, Miller RG, Enright NJ, Fontaine JB, Merritt DJ, Ooi MKJ, Ruthrof KX, Miller BP (2020) Seed dormancy interacts with fire seasonality mechanisms. Trends in Ecology & Evolution 35, 1057-1059.
| Crossref | Google Scholar |

Taylor NJ (1987) ‘Ecological aspects of Nassella Tussock (Stipa trichotoma).’ (Botany Division, Department of Scientific and Industrial Research: Lincoln, New Zealand)

Valette JC, Gomendy V, Marechal J, Houssard C, Gillon D (1994) Heat-transfer in the soil during very low-intensity experimental fire – the role of duff and soil-moisture content. International Journal of Wildland Fire 4, 225-237.
| Crossref | Google Scholar |

Vaughton G, Ramsey M (2001) Relationships between seed mass, seed nutrients, and seedling growth in Banksia cunninghamii (Proteaceae). International Journal of Plant Sciences 162, 599-606.
| Crossref | Google Scholar |

Vermeire LT, Rinella MJ (2009) Fire alters emergence of invasive plant species from soil surface-deposited seeds. Weed Science 57, 304-310.
| Crossref | Google Scholar |

Walters C, Hill LM, Wheeler LJ (2005) Dying while dry: kinetics and mechanisms of deterioration in desiccated organisms. Integrative and Comparative Biology 45, 751-758.
| Crossref | Google Scholar |

Wehmeyer N, Hernandez LD, Finkelstein RR, Vierling E (1996) Synthesis of small heat-shock proteins is part of the developmental program of late seed maturation. Plant Physiology 112, 747-757.
| Crossref | Google Scholar |

Wells MJ, De Beer H (1987) ‘Nassella Tussock. Farming in South Africa.’ pp. 1–3. (Department of Agriculture and Water Supply: Pretoria, South Africa)

Yan H, Liu G (2021) Fire’s effects on grassland restoration and biodiversity conservation. Sustainability 13, 12016.
| Crossref | Google Scholar |

Zirondi HL, Silveira FAO, Fidelis A (2019) Fire effects on seed germination: heat shock and smoke on permeable vs impermeable seed coats. Flora: Morphology, Distribution, Functional Ecology of Plants 253, 98-106.
| Crossref | Google Scholar |