Journal of Botany

Journal of Botany / 2013 / Article

Research Article | Open Access

Volume 2013 |Article ID 712405 |

Gurveen Kaur, Bhupinder Pal Singh, Avinash Kaur Nagpal, "Phenology of Some Phanerogams (Trees and Shrubs) of Northwestern Punjab, India", Journal of Botany, vol. 2013, Article ID 712405, 10 pages, 2013.

Phenology of Some Phanerogams (Trees and Shrubs) of Northwestern Punjab, India

Academic Editor: William K. Smith
Received23 Jan 2013
Revised26 Apr 2013
Accepted19 May 2013
Published25 Jun 2013


Plants perform various vegetative and reproductive functions throughout the year in order to persist in their habitats. The study of these events including their timing and how the environment influences the timing of these events is known as phenology. This study of the timing of seasonal biological activities of plants is very important to know about plant’s survival and its reproductive success. The variation in the phenological activities is due to change in different abiotic conditions. This paper deals with the study of phenological activities like bud formation, flowering time, fruiting time, and seed formation for some leguminous plants of Amritsar, Punjab (a state in the northwest of India) for three consecutive years from 2009 till 2011.

1. Introduction

The timing of various phenological activities such as germination, bud break, flowering, fruit dehiscence, and leaf drop is important for survival and reproductive success of many plant species. Abiotic environmental conditions such as rain, change in temperature, presence/absence of pollinators, competitors, and herbivores have been shown to play a significant role in timing of various phenological events [16]. Natural selection has also been considered to play some role in determining the phenological patterns of plant species [7]. Phenological studies are also important in understanding species interrelations and their interaction with the environment. Variations in phenophases among individuals of the same species or different species have been linked to environmental perturbations [8].

Considerable amount of phenological data is available on different plant species from different parts of the world including tropical savanna and semideciduous forest of Venezuelan Ilanos (South America) [9], dry tropical forest in Ghana [10], NE Spain [1113], Panama [14], Mexico [15], tropical rain forest in Malaya [16], semiarid grassland in the Rock mountain, USA [17], and tibetan plateau [18].

A number of studies on phenology of different plant species from different parts of India have also been undertaken which include those from a subtropical humid forest in North-Eastern India [19, 20], Kumaun Himalayan forests [21, 22], deciduous forest of Bandipur in peninsular India [23], Shervaroys, Southern India [24], tropical moist forest of Western Ghats in Karnataka [25], Hathinala Forest in Uttar Pradesh [26], alpine expanse of North-West Himalaya [27], Orissa coast [28], tropical montane forests in the Nilgiris [8], Kolhapur region (Maharashtra) [29], and Katerniaghat wildlife sanctuary situated in the Himalayan Terai region in Uttar Pradesh [30], Northeastern India [31]. However, no such information is available on plants of Punjab plains, hence we initiated phenological studies in trees and shrubs of this region of India. To begin with, we have compiled information on fifteen leguminous species from Amritsar.

The family leguminosae is a large and economically important family of flowering plants and has traditionally been divided into three subfamilies Papilionoideae (Faboideae), Caesalpinioideae, and Mimosoideae. These have been recognized as independent families Fabaceae (Papilionaceae), Caesalpiniaceae, and Mimosaceae in several recent systems of classification.

The present paper deals with phenological observations of fifteen leguminous plants growing at four different sites in Amritsar over a period of three years from 2009 till 2011 as these sites represent most of the plant diversity of this region.

2. Materials and Methods

2.1. Study Area

The Amritsar district is located in northwestern part of the Punjab state and lies between 31°28′30′′ to 32°03′15′′ north latitude and 74°29′30′′ to 75°24′15′′ east longitude. Total area of the district is 5056 km2 with tropical dry deciduous type of vegetation [32]. Natural vegetation is fragmented and is at present available only in narrow strips and patterns.

Amritsar has a semiarid climate, typical of northwestern India and experiences four seasons primarily:(i)winter season (December to February) with temperature ranges from 4°C (39°F) to about 19°C (66°F);(ii)summer season (April to June) where temperatures can reach 45°C (113°F); (iii)monsoon season (July to September);(iv)postmonsoon season (September to October).

There is a transitional period between winter and summer in March and early April (called as spring), as well as a transitional season between postmonsoon season and winter in October and November (called as autumn). Annual rainfall in Amritsar is about 680 millimetres (ground water information booklet, Amritsar district, Punjab by Central Ground Water Board, Ministry of Water Resources, Government of India, north western region, Chandigarh).

The whole area of Amritsar was surveyed and four different sampling sites, that is, Guru Nanak Dev University (G), Sakatri Bagh (S), Maharaja Ranjit Singh Park (M), and Ranjit Avenue (R) were selected for data collection. These sites were chosen as they represent most of the plant diversity of Amritsar. Figure 1 shows the location of four sites on the map of Amritsar. The maps were downloaded from Maps of India and Google images, and the climatic data of Amritsar was obtained from the wunderground website ( This weather station (VIAR) is located at Raja Sansi International Airpot, Amritsar at an elevation of 234 m. Table 1 shows the minimum, mean, and maximum temperature values from January to December for three consecutive years from 2009 to 2011 of Amritsar.



Table 2 lists fifteen plant species selected for the present study along with their family, sampling site, growth form, and leaf habit. The data for each species was collected from a minimum of two sampling sites mentioned in Table 2. At each site, one mature and healthy plant from the population of that species was fixed as reference for the study. The observations were made on the marked plant and 10–15 of its closest neighbours (minimum 6 plants if more plants were not available for a particular plant species at a particular site) for a period of 3 years starting from January 2009 up to December, 2011. This selection regime was based on a study by Pilar and Gabriel [12]. The areas with the plants under study were visited daily to record presence/absence of different phenological events or phenophases: flower bud formation (B), flowering (FL), fruit setting (FR), and seed set and dispersal (S). The information for the initial date and the last date when these various phenophases were observed was recorded. A phenophase was considered to be active in the population just when it was observed in at least 5% of the crown in a minimum of 20% of the studied plants [12]. Phenophase calendars for each species were prepared and were studied for the interpretation of the overall results. For the whole set of studied species, the frequency of occurrence of different phenophases in each month was calculated.

S. No.SpeciesAbbreviationFamilySampling site*Growth formLeaf habit

1Bauhinia variegata Linn.BvaCaesalpiniaceaeG, S, M, RTD
2Caesalpinia pulcherrima (Linn.) Sw.CpuCaesalpiniaceaeG, M, RSE
3Cassia fistula Linn.CfiCaesalpiniaceaeG, S, M, RTD
4Cassia glauca Lam.CglCaesalpiniaceaeG, S, RSE
5Cassia siamea Lamk.CsiCaesalpiniaceaeG, RTE
6Delonix regia Rafin.DreCaesalpiniaceaeG, S, MTD
7Parkinsonia aculeata Linn.PacCaesalpiniaceaeG, RTD
8Acacia auriculiformis A. Cunn.AauMimosaceaeG, M, RTE
9Acacia nilotica DelileAniMimosaceaeG, RTE
10Albizia lebbeck Benth.AleMimosaceaeG, STD
11Calliandra tweedii Benth.CtwMimosaceaeG, RSE
12Prosopis juliflora DC.PjuMimosaceaeG, S, MTE
13Abrus precatorius Linn.ApePapilionaceaeG, S, RCD
14Butea monosperma (Lam.) KuntzeBmoPapilionaceaeG, RTD
15Dalbergia sissoo Roxb.DsiPapilionaceaeG, S, M, RTD

Sampling sites shown in Figure 1.

3. Results

The results on percentage of 15 plant species taken all together showing timing of different phenophases (Buds, Flowers, Fruits, and Seeds) during the study period are shown in Figure 2. This figure reveals that percentage of plant species exhibiting each phenophase, that is, buds, flowers, fruits, and seeds showed almost a similar trend for three consecutive years within each phenophase. Bud formation showed a peak in the beginning of summer (60%) and another small peak during late monsoon and was almost evenly distributed through the rest of the year for all the three years. Similar trend was observed for flowering which also showed a peak (66.67%) during beginning of summer and another small peak (53.33%) during postmonsoon period for all the three years. Maximum percentage of plant species showing fruiting was observed in the months of March, April, and May (60%) which resulted in maximum seed set in the months of June, July, and August during the study period. Comparison of results on observations of flowering in different plant species during the three consecutive years 2009, 2010, and 2011, reveals that maximum percentage of plant species (66.67%) showing flowering was observed in the month of April during 2011.

Figure 3 shows phenological patterns of individual plant species studied. For each plant species, the whole period of appearance of different phenophases-like bud formation, flowering, fruiting, and seed set has been indicated for three consecutive years. The study reveals high phonological diversity for different phenophases studied among fifteen plant species. However, for individuals of the same species, no differences in the appearance of different phenophases were observed.

During the study period, it was observed that some species like Bauhinia variegata Linn., Caesalpinia pulcherrima (Linn.) Sw., Cassia glauca Lam., Cassia siamea Lamk., and so forth showed conspicuous buds (2–4 weeks) before flowering, but in case of Dalbergia sissoo Roxb bud formation was observed just few days (less than a week) before prominent flowering was recorded. Most of the species flowered from spring to late summer (e.g., Parkinsonia aculeata Linn. and Acacia auriculiformis A. Cunn.). Butea monosperma (Lam.) Kuntze exhibited flowering during the monsoon and postmonsoon period only. Some of the species that showed flowering during winter months extending to early summer included Caesalpinia pulcherrima (Linn.) Sw., Cassia siamea Lamk., and Delonix regia Rafin. Variation in the flowering time period was observed for different species ranging from 2 months (Abrus precatorius Linn.) to 7 months (Cassia glauca Lam.). Similarly the variation in fruiting period was observed from 3 months as in the case of Cassia siamea Lamk., and so forth, to have fruiting almost throughout the year as for Dalbergia sissoo Roxb. By the end of summer, the seeds of most of the plant species were mature and ready for dispersal. There were two time periods in the year when leaf shedding was observed, that is, in summer and in the autumn depending on the type of leaf habit of that plant species.

4. Discussion

Our study reveals high phenological diversity for the four phenological patterns (buds, flowers, fruits, and seeds) among fifteen leguminous plant species growing in Amritsar under similar environmental conditions for the three consecutive years, that is, 2009, 2010, and 2011. Changes in plant phenological patterns have been associated with the species specific plant structural architecture, availability and transfer of nutrients [33], plant growth rates [34], temperature [35], and water [36].

A comparison of observations on flowering time for the three years under study reveals an advancement of flowering time by about 2–4 weeks in the year 2010 for some species like Acacia nilotica Delile, Abrus precatorius Linn., Bauhinia variegata Linn., Dalbergia sissoo Roxb., Delonix regia Rafin., and Parkinsonia aculeata Linn. as compared to that observed in 2009 (Figure 3). This change in phenological shift can be attributed to increase in temperature in 2010 as compared to that reported for 2009 (Table 1). The total length of flowering period was extended by 2–4 weeks in 2010-11 as compared to 2009 for species like Bauhinia variegata Linn., Caesalpinia pulcherrima (Linn.) Sw., Cassia fistula Linn., Parkinsonia aculeata Linn., Acacia nilotica Delile, Calliandra tweedii Benth., and Prosopis juliflora DC.

Some other studies have also demonstrated an association of an advancement in flowering date with climate change. One study has reported an increase in the mean terrestrial surface temperature by more than 0.2°C per decade ever since 1970 [37]. A number of other studies have shown an advancement of phenological events as a result of increase in temperature [3841]. With the increase in the temperature, most of the species showed earlier flowering time period [39] and even increase in their time period of flowering (e.g., Bauhinia variegate Linn., Prosopis juliflora DC.). Similarly early flowering was observed for 24 out of the 32 plant species studied in a semiarid grassland by Lesica and Kittelson [17].

The period of maximum activity of bud formation in the months of spring and the flowering period (started in spring and extended to summer and the beginning of autumn) coincided with the observations of Pilar and Gabriel [12]. Flower development dates have been shown to be synchronous among individuals of the same plant species studied which seems to be important in increasing the chances of outcross pollinations as suggested by Ollerton and Lack [42].

These changes in the phenological patterns can result in adverse effects on insect pollinators as well as herbivores (if the plant species is present in barren or wild areas) that depend on those species for food [43, 44]. The changes in phenological patterns of plant’s response to different temperature and rainfall availability have been shown to be species specific [45, 46]. Hence changes in vegetation community species composition might also be responsible for changes in the phenology of the studied plants. The present study reveals that different plants of the same family (Leguminosae) flower at different times during the same year growing at same location under similar environmental conditions which can be attributed to species-specific plant structural architecture.

5. Conclusion

The present study reveals high phenological diversity for four different phenophases among fifteen leguminous plant species growing in Amritsar with tropical dry deciduous type of vegetation. This study would be of great help in knowing the timing of different phenophases of the studied plants which can be of interest to people of this region (or where similar climatic conditions prevail) who wish to plan their gardens and wish to have flowers in their gardens round the year. So, they can select plants which flower during different parts of the year. This type of study can provide important insights into the biology of the plants concerned and reveal phenological pattern of surveyed species. This study would also be of great help for comparison over long duration of time. For example, to see if there is any change in the phenological patterns of the same plant species in next 10 or so years. Such comparative study could not be possible at this time since no relevant literature is available for this region.


The authors thank Department of Science and Technology, Government of India, for INSPIRE Fellowship to Ms. Gurveen Kaur.


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Copyright © 2013 Gurveen Kaur et al. This is an open access article distributed under the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.

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