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Modeling the Emergence and Growth of Alligatorweed at Different Field Capacity Levels

Modelando a Emergência e o Crescimento da Erva-de-Jacaré em Diferentes Níveis de Capacidade de Campo

ABSTRACT:

A study focusing on different field capacity levels was planned in the Weed Science Lab, Department of Agronomy, University of Agriculture Faisalabad. Fresh alligatorweed was harvested from the Agronomy fields and cuttings (2 cm length) were made from it. These cuttings were placed at 25%, 50%, 75% and 100% field capacity levels in pots for 25 days. The results of the experiments revealed that at all field capacity levels, fragments of alligatorweed were able to sprout and grow. Increased moisture levels significantly increased the emergence ability and survival of the alligatorweed plants upto a certain level. Compared with the control (25% FC), emergence time of the sprouts in the maximum moisture regime (100% of FC) decreased by 40% (12.94 days vs.7.17 days). By contrast, the survival rate of the fragments decreased by 60% (5 vs. 1.75) although survival and growth rate increased at first with 50% FC and 75% FC. Maximum sprouting and growth were found at 50% field capacity. Field capacity does affect the sprouting capacity of alligatorweed fragments but it has only a little influence on growth parameters. The results suggest that alligatorweed can sustain dry conditions to a great extent and also has the ability to sprout and grow in fully submerged soils.

Keywords:
humidity soil conditions; invasive weed; seedling growth

RESUMO:

Foi conduzido um estudo com foco nos diferentes níveis de capacidade de campo no Laboratório de Ciências de Plantas Daninhas do Departamento de Agronomia da University of Agriculture Faisalabad. Erva-de-jacaré fresca foi colhida em campo para a preparação de estacas (2 cm de comprimento). Essas estacas foram mantidas em vasos por 25 dias, em níveis de 25%, 50%, 75% e 100% da capacidade de campo. Os resultados dos experimentos revelaram que, em todos os níveis de capacidade de campo, houve crescimento e brotação dos fragmentos de erva-de-jacaré. A elevação da umidade levou a aumento significativo da capacidade de emergência e sobrevivência das plantas de erva-de-jacaré até um certo nível. Comparado com o controle (25% CC), o tempo de emergência dos brotos no regime de umidade máxima (100% da CC) diminuiu em 40% (12,94 dias contra 7,17 dias). Já a taxa de sobrevivência dos fragmentos diminuiu em 60% (5 contra 1,75), embora a taxa de sobrevivência e o crescimento tenham aumentado inicialmente com 50% de CC e 75% de CC. Os valores máximos de crescimento e brotação foram observados a 50% da capacidade de campo. A capacidade de campo afeta a capacidade de brotação dos fragmentos de erva-de-jacaré, mas tem pouca influência nos parâmetros de crescimento. Os resultados sugerem que a erva-de-jacaré é capaz de suportar bem a escassez de água, assim como consegue brotar e crescer em solos totalmente submersos.

Palavras-chave:
condições de umidade do solo; planta daninha invasora; crescimento de plântulas

INTRODUCTION

Biotic invasion is considered as one of the top five causes of global biodiversity loss and it is increasing on a daily basis because of tourism and globalization. Invasive species may drive local native species to extinction via competitive exclusion, niche displacement, or hybridization with related native species. Therefore, in addition to their economic ramifications, alien invasions may result in extensive changes in the structure, composition and global distribution of the biota of sites of introduction, ultimately leading to the homogenization of the world’s fauna and flora and loss of biodiversity (Odendaal et al., 2008Odendaal LJ, Haupt TM, Griffiths CL. The alien invasive land snail Theba pisana in the West Coast National Park: Is there cause for concern? Koedoe. 2008;50(1):93-8.).

Alternanthera philoxeroides, commonly known as alligatorweed, is an emergent invasive weed in Pakistan. Alligatorweed is one of the invasive weeds which poses serious threats to native plant populations and cropping systems throughout the world (Khan et al., 2012Khan N, Khan NW, Khan SA, Khan MA, Marwat KB. Combined effect of nitrogen fertilizers and herbicides upon maize production in Peshawar. Journal of Animal and Plant Science. 2012;22(2S):12-8. ). It is a potentially devastating weed that grows in water and on land, affecting both waterways and floodplain areas. It is listed as a weed of national significance in Australia (Reid et al., 2009Reid AM, Morin L, Downey PO, French K, Virtue JG. Does invasive plant management aid the restoration of natural ecosystems? Biol Conserv. 2009;142(10):2342-9.). Alligatorweed disrupts the aquatic environment by blanketing the surface and hence impeding the penetration of light. Such blanketing can also impede gaseous exchange (sometimes leading to anaerobic conditions) which adversely affects aquatic flora and fauna. It also competes with and displaces native flora alongside rivers and creek banks and in wetlands (Ensbey and van Oosterhout, 2001Ensbey R, van Oosterhout E. Alligator weed. Invasive Species Unit, Biosecurity NSW; 2001.). It is generally considered a water weed but it can also disrupt terrestrial cropping systems, resulting in reduced yield of all the crops because it competes with crops and releases harmful chemicals, called allelochemicals. Yield losses of 19-60% have been reported as a result of A. sessilis and A. philoxeroidesin field crops(Tanveer et al., 2013aTanveer A, Khaliq A, Siddiqui MH. A review on genus Alternanthera weeds implications. Pak J Weed Sci Res. 2013a;19(1):53-8.).

Alligatorweed is becoming a potential threat in rice-based cropping systems in Pakistan. Conventional weed control methods such as flooding have proved ineffective to control/suppress the growth of alligatorweed and have resulted in a greater loss of water. To reduce his water loss, different techniques are now being applied, e.g., alternate wetting and drying. However, this change will certainly affect the behavior of alligatorweed, too. Previous studies have addressed the behavior and impact of alligatorweed in aquatic ecosystems, yet very little information is available on its dynamics in terrestrial ecosystems, where there may even be drought conditions as well(Bassett et al., 2012Bassett I, Paynter Q, Hankin R, Beggs JR. Characterising alligator weed (Alternanthera philoxeroides; Amaranthaceae) invasion at a northern New Zealand lake. NZ J Ecol. 2012;36(2):216-22). An understanding of seed germination ecology of weeds can assist in predicting their potential distribution and developing effective management strategies (Tanveer et al., 2013bTanveer A, Mumtaz K, Javaid M, Chaudhry M, Balal R, Khaliq A. Effect of ecological factors on germination of horse purslane (Trianthema portulacastrum). Planta Daninha. 2013b;31(3):587-97.).

There is a great deal of controversy about the water requirement and behavior of alligatorweed in dry environments. Therefore, the objectives of the present research were to find out which water level in the field favors growth and which level restricts it, and to assess the behavior of alligatorweed under different water management techniques.

MATERIAL AND METHODS

Sandy clay loam soil was collected from experimental fields of the Agronomy Department, UAF, Pakistan. The soil sample were oven-dried for 24 hours at 105 oC and then weighed. An average was calculated to find out total moisture content. Three oven-dried samples were used to find out saturation percentage, which was estimated by measuring the total volume of distilled water used in making fully saturated paste, and then an average was calculated. The following formula was then used to calculate field capacity:

Field capacity (FC) = Saturation percentage/2

Initial weight of the soil in the plastic pots and the respective water content had been previously determined, hence the current weight of every plastic pot after saturation represents 100%, 75%, 50% and 25% field capacity. Field-grown whole plants of alligatorweed (with almost the same age) were uprooted by using random sampling techniques from fields of the Agronomy Department, University of Agriculture Faisalabad, Pakistan in 2015. Equal-sized cuttings (2 cm) with a single node were made from alligatorweed stems. Pots (15.2 cm top diameter, 11.2 cm bottom diameter and 11.8 cm depth) were used to sow the stem cuttings. CRD (completely randomized design) with four repeats was used to layout the experiment. Ten equal-sized cuttings (2 cm) of field-grown alligatorweed were placed evenly in pots and given field capacity was maintained. Weight was maintained by adding water three times a day (in the morning, noon and evening). The pots were placed in an open environment and daily weather data (day to day) were collected from Agricultural Meteorology Cell, UAF, Pakistan. Mean daily maximum and minimum temperatures recorded were 34.9 oC and 27 oC, respectively. Sprouting count was recorded daily. Twenty-five-day-old seedlings were uprooted and washed with water and their shoot, root lengths and fresh weights were recorded. Than plants were dried in an electrical oven for 48 hours at 70 oC and afterwards dry weight of the plants was noted.

Parameters recorded on alligatorweed sprouting and seedling growth were sprouting percentage (SP) (AOSA, 1990Association of Official Seed Analysis - AOSA. Rules for testing seeds. J Seed Technol. 1990;12:1-112.), sprouting index (SI) (AOSA, 1990Association of Official Seed Analysis - AOSA. Rules for testing seeds. J Seed Technol. 1990;12:1-112.), mean sprouting time (MST) (Ellis and Roberts, 1981Ellis R, Roberts E. The quantification of ageing and survival in orthodox seeds. Seed Sci Technol. 1981;9:373-409.), time to 50% sprouting (Coolbear et al., 1984Coolbear P, Francis A, Grierson D. The effect of low temperature pre-sowing treatment on the germination performance and membrane integrity of artificially aged tomato seeds. J Exp Bot. 1984;35(11):1609-17), root length per plant (cm), shoot length per plant (cm), shoot dry weight per plant (mg), root dry weight per plant (mg), seedling dry weight per plant (mg), seedling vigor index (SVI) and root-shoot ratio (RSR).

Procedures for recording observations of lab experiments

Sprouting percentage was determined by counting daily sprouting up to twenty-five days. After this period, observation was concluded. Sprouting was observed daily according to the AOSA methods (1990) and converted into sprouting percentage by the following formula (Equation 1):

S P = S p r o u t e d c u t t i n g s T o t a l c u t t i n g s × 100 (eq. 1)

Sprouting Index (SI) was calculated by using the formula (Equation 2) as described by AOSA (1990Association of Official Seed Analysis - AOSA. Rules for testing seeds. J Seed Technol. 1990;12:1-112.):

I = N o . o f s p r o u t e d c u t t i n g s D a y s o f f i r s t c o u n t + + N o . o f s p r o u t e d c u t t i n g s D a y s o f f i n a l c o u n t (eq. 2)

Mean sprouting time was calculated according to the equation of Ellis and Roberts (1981Ellis R, Roberts E. The quantification of ageing and survival in orthodox seeds. Seed Sci Technol. 1981;9:373-409.).

M S T = D n n × 100 (eq. 3)

where n is the number of cuttings that had sprouted on day “D” and D is the number of days counted from the beginning of sprouting. Time to 50% sprouting (T50) was calculated according to the formula (Equation 4) of Coolbear et al. (1984Coolbear P, Francis A, Grierson D. The effect of low temperature pre-sowing treatment on the germination performance and membrane integrity of artificially aged tomato seeds. J Exp Bot. 1984;35(11):1609-17)

T 50 = t i ( N + 1 / 2 - n i ) ( t j - t i ) ( n j - n i ) (eq. 4)

as modified by Farooq et al. (2005Farooq M, Basra S, Ahmad N, Hafeez K. Thermal hardening: A new seed vigor enhancement tool in rice. J Integr Plant Biol. 2005;47(2):187-93.) (Equation 5).

T 50 = t i ( N / 2 - n i ) ( t j - t i ) ( n j - n i ) (eq. 5)

where N is the final number of sprouted cuttings and nj and ni are the cumulative number of cutting sprouted by adjacent counts at times tj and ti, respectively, where ni<N/2 <nj. Sprouting energy (SE) is the percentage of sprouted cuttings as recorded on the 4th day after sowing, relative to the total number of cuttings which were sown (Ruan et al., 2002Ruan S, Xue Q, Tylkowska K. The influence of priming on germination of rice (Oryza sativa L.) seeds and seedling emergence and performance in flooded soil. Seed Sci Technol. 2002;30(1):61-7.).

Seedling growth parameters

The survived plants were uprooted from each pot under wet conditions. Shoot length is determined from the root-shoot junction to the top of the seedling. Then average shoot length was determined. The separated roots were taken and their lengths were measured in cm. Then average root length was calculated. After that, the separated roots/shoots of all seedlings were oven-dried at 70 oC for 48 h and then weighed. This weight was used to calculate average root/shoot dry weight per plant in grams. Shoot and root dry weights of all seedlings from each treatment were summed and then used to calculate average seedling dry weight. Sprouting percentage and seedling length were used to calculate seedling vigor index (SVI) by the following formula (Equation 6) as described by Orchard (1977Orchard T. Estimating the parameters of plant seedling emergence. Seed Sci Technol. 1977; 5(1): 61-69. ):

S V I = s e e d l i n g l e n g t h c m × s p r o u t i n g p e r c e n t a g e (eq. 6)

Statistical analysis

The average data collected in this study were analyzed statistically by using Kruskal-Wallis One-Way analysis of variance techniques with computer software Statistix 8.1. The Kruskal-Wallis all-pairwise comparison test was applied at 5% probability level to test the significance of treatment means. The experiment was repeated twice. A simple linear regression model was used to check the effect of burial depths on sprouting and seedling growth response of alligatorweed.

RESULT AND DISCUSSION

Effect of different percentages of field capacity levels (FCL) on alligatorweed sprouting parameters

FCL percentage significantly affected sprouting and survival characteristics of alligatorweed (Table 1). At first, increased FCL enhanced the survival and sprouting of alligatorweed, as shown in (Figure 1A, B, C, D) and (Figure 2A, B, C, D). In the 26 day testing period, maximum final sprouting count (10) (Figure 1c) was recorded at 50% field capacity (FC) followed by that of 75% FC, with a sprouting count of 7.5. Minimum sprouting was recorded at 100% FC.

Table 1
Analysis of variance for all the study parameters

Figure 1
Means of emergence parameters of alligatorweed by different field capacity levels.

Figure 2
Means of emergence parameters of alligatorweed by different field capacity levels.

FCL significantly affected time to start sprouting (Figure 1d). Maximum time taken to start sprouting (7.5 days) was recorded at 25% FC while minimum time (2.75 days) was recorded at 50% FC. Maximum T50 (13.52 days) was recorded with 25% FC followed by that of 100% FC (6.75 days), 75% FC (76.36 days) and 25% FC(4.82 days) (Figure 1B). Minimum mean sprouting time (Figure 1A) was recorded at 50% FC (5.9 days), which was statically similar to the mean sprouting time recorded for 100% FC(7.17 days) and 75% FC (7.57 days). As far as sprouting index (Figure 2A) and percentages (Figure 2B) are concerned, there were significant differences between all the treatments. Maximum EI (2.06) and EP (100) were recorded when alligatorweed was grown at 50% FC, followed by growth at 75% FC, 25% FC and 100% FC, respectively.

Effect of field capacity water content percentages on alligatorweed seedling growth

(Figure 3A, B) and (Figure 4A, B, C, D) showed seedling growth response of alligatorweed to different field capacity (FC) percentages. FC percentages significantly affected all the seedling growth parameters apart from root-shoot ratio (Table 1; Figure 4D). Maximum shoot length (4.23 cm) was recorded for 50% FC, which was statically higher than all other treatments (Figure 3A). This was followed by the shoot length value recorded for 75% FC (3.21 cm). Minimum shoot length (1.13 cm) was found at 100% of FC. Similar results were found for root length (Figure 3B), root dry weight (Figure 4b), seedling dry weight (Figure 4C) and shoot dry weight (Figure 4A). Seedling vigor index was also higher for 50% FC (1095.1) followed by the seedling vigor index recorded for 75% FC (490) and 25% FC (309).

Figure 3
Means of seedling growth of alligatorweed by different field capacity levels.

Figure 4
Means of seedling growth parameters of alligatorweed by different field capacity levels.

Increased moisture levels significantly increased the sprouting ability and survival of the alligatorweed plants up to a certain level. Compared with the control (25% of FC), sprouting time of the clonal fragments in the maximum moisture regime (100% FC) decreased by 40% (12.94 days vs 7.17 days). However, the survival rate of the fragments also decreased by 60% (5 vs. 1.75) although survival and growth rate increased at first with 50% of FC and 75% of FC. Previous studies also found that an increase in moisture regime increased the sprouting and survival of Amaranthus spinosus and Leptochloa chinensis (Chauhan and Abugho, 2013Chauhan BS, Abugho SB. Effect of water stress on the growth and development of Amaranthus spinosus, Leptochloa chinensis, and rice. Am J Plant Sci. 2013;4(5):989). They conducted trails on water stress treatments (12.5%, 25%, 50%, 75%, and 100% field capacity) and found that both weed species survived in all the treatments. Both weed species produced a significant number of tillers/branches and leaves even at the lowest soil water content. Soil water content to achieve 50% of the maximum aboveground biomass was 47% - 50% field capacity for rice, but 39% and 31% field capacity for A. spinosus and L. chinensis, respectively.

Quackgrass and foxtail barley had significantly greater sprouting when moisture levels remained between FC and one-third of the FC than when they fluctuated between FC and one-sixth of the FC (Boyd and van Acker, 2003Boyd NS, van Acker RC. The effects of depth and fluctuating soil moisture on the emergence of eight annual and six perennial plant species. Weed Sci. 2003;51(5):725-30). The impact of soil moisture on sprouting varies among weed species, and field conditions may differ spatially and temporally, depending on rainfall, temperature and soil type. Plant-available water in the soil lies between field capacity (-0.03 MPa) and permanent wilting point (-1.5 MPa) (Miller and Donahue, 2004Miller R, Donahue R. Soils in our environment. 11th.ed. New Jersey: Prentice Hall; 2004. Cap.1, Soil water properties; p.62-97). Sprouting of T. portulacastrum decreased by decreasing field capacity. Decreased sprouting under low moisture conditions was probably due to lack of enough water for seed imbibitions and softening (Tanveer et al., 2013cTanveer A, Tasneem M, Khaliq A, Javaid M, Chaudhry M. Influence of seed size and ecological factors on the germination and emergence of field bindweed (Convolvulus arvensis). Planta Daninha. 2013c;31(1):39-51.).

Field capacity actually affects the sprouting capacity of alligatorweed stolons but it has only little influence on RSR, which shows very little effect of FC on growth parameters of alligatorweed. One possible explanation for the irresponsiveness of the species to field capacity is that alligatorweed quickly comes out of soil and starts to transpire as much water as it can, hence itshows no difference at almost at all levels. Late-sprouted plants may enhance the photosynthesis rate by compensating for the water loss which results from delayed sprouting time (Lu and Ding, 2009Lu X, Ding J. Flooding compromises compensatory capacity of an invasive plant: implications for biological control. Biol Invas. 2009;12(1):179-89.). Dissimilar plant compensatory capacity, affected by flooding, may explain the different biological control efficacy of alligatorweed in aquatic and terrestrial habitats. Submergence decreased the growth of alligatorweed but allowed 100% survival. Because of increased shoot length when the plants were submerged at the 0.5 m depth for 2 weeks, 62.5% of themgrew above the water (Fan et al., 2015Fan S, Yu H, Liu C, Yu D, Han Y, Wang L. The effects of complete submergence on the morphological and biomass allocation response of the invasive plant Alternanthera philoxeroides. Hydrobiologia. 2015;746(1):159-69.). Elongation of shoots and internodes, higher specific leaf area ratio, leaf weight ratio and stem diameters, development of new leaves (not at depths deeper than 1.0 m) and adventitious roots at all water depths were tolerance strategies of alligatorweed in response to submergence, infect short periods of drying in-between complete flooding may enhance its growth rather than complete flooding or complete drying.

These strategies suggest that alligatorweed can bear significantly high levels of water stress and can survive even at lower field capacity levels. This may increase the invasiveness of alligatorweed and make it very adaptable to heavily disturbed habitats. Based on all these results, it can be concluded that alligatorweed will spread rapidly under the current climatic conditions of Pakistan and will cause greater yield losses in all the crops.

ACKNOWLEDGEMENTS

This study is a part of the main author’s thesis research work for Ph.D. degree at the Department of Agronomy, University of Agriculture, Faisalabad, Pakistan. The authors are thankful to the financial support of the Higher Education Commission, Government of Pakistan, under the Indigenous Ph.D. 5000 Fellowships) Program.

REFERENCES

  • Association of Official Seed Analysis - AOSA. Rules for testing seeds. J Seed Technol. 1990;12:1-112.
  • Bassett I, Paynter Q, Hankin R, Beggs JR. Characterising alligator weed (Alternanthera philoxeroides; Amaranthaceae) invasion at a northern New Zealand lake. NZ J Ecol. 2012;36(2):216-22
  • Boyd NS, van Acker RC. The effects of depth and fluctuating soil moisture on the emergence of eight annual and six perennial plant species. Weed Sci. 2003;51(5):725-30
  • Chauhan BS, Abugho SB. Effect of water stress on the growth and development of Amaranthus spinosus, Leptochloa chinensis, and rice. Am J Plant Sci. 2013;4(5):989
  • Coolbear P, Francis A, Grierson D. The effect of low temperature pre-sowing treatment on the germination performance and membrane integrity of artificially aged tomato seeds. J Exp Bot. 1984;35(11):1609-17
  • Ellis R, Roberts E. The quantification of ageing and survival in orthodox seeds. Seed Sci Technol. 1981;9:373-409.
  • Ensbey R, van Oosterhout E. Alligator weed. Invasive Species Unit, Biosecurity NSW; 2001.
  • Fan S, Yu H, Liu C, Yu D, Han Y, Wang L. The effects of complete submergence on the morphological and biomass allocation response of the invasive plant Alternanthera philoxeroides Hydrobiologia. 2015;746(1):159-69.
  • Farooq M, Basra S, Ahmad N, Hafeez K. Thermal hardening: A new seed vigor enhancement tool in rice. J Integr Plant Biol. 2005;47(2):187-93.
  • Khan N, Khan NW, Khan SA, Khan MA, Marwat KB. Combined effect of nitrogen fertilizers and herbicides upon maize production in Peshawar. Journal of Animal and Plant Science. 2012;22(2S):12-8.
  • Lu X, Ding J. Flooding compromises compensatory capacity of an invasive plant: implications for biological control. Biol Invas. 2009;12(1):179-89.
  • Miller R, Donahue R. Soils in our environment. 11th.ed. New Jersey: Prentice Hall; 2004. Cap.1, Soil water properties; p.62-97
  • Odendaal LJ, Haupt TM, Griffiths CL. The alien invasive land snail Theba pisana in the West Coast National Park: Is there cause for concern? Koedoe. 2008;50(1):93-8.
  • Orchard T. Estimating the parameters of plant seedling emergence. Seed Sci Technol. 1977; 5(1): 61-69.
  • Reid AM, Morin L, Downey PO, French K, Virtue JG. Does invasive plant management aid the restoration of natural ecosystems? Biol Conserv. 2009;142(10):2342-9.
  • Ruan S, Xue Q, Tylkowska K. The influence of priming on germination of rice (Oryza sativa L.) seeds and seedling emergence and performance in flooded soil. Seed Sci Technol. 2002;30(1):61-7.
  • Tanveer A, Khaliq A, Siddiqui MH. A review on genus Alternanthera weeds implications. Pak J Weed Sci Res. 2013a;19(1):53-8.
  • Tanveer A, Mumtaz K, Javaid M, Chaudhry M, Balal R, Khaliq A. Effect of ecological factors on germination of horse purslane (Trianthema portulacastrum). Planta Daninha. 2013b;31(3):587-97.
  • Tanveer A, Tasneem M, Khaliq A, Javaid M, Chaudhry M. Influence of seed size and ecological factors on the germination and emergence of field bindweed (Convolvulus arvensis). Planta Daninha. 2013c;31(1):39-51.

Publication Dates

  • Publication in this collection
    15 June 2020
  • Date of issue
    2020

History

  • Received
    28 Sept 2017
  • Accepted
    15 Dec 2017
Sociedade Brasileira da Ciência das Plantas Daninhas Departamento de Fitotecnia - DFT, Universidade Federal de Viçosa - UFV, 36570-000 - Viçosa-MG - Brasil, Tel./Fax::(+55 31) 3899-2611 - Viçosa - MG - Brazil
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