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Cygnus (2013) 1: 12-18 DOI [21294131, 21114466, 21320437] RESEARCH ARTICLE__________________________________ Rainfall has an effect on the length of the boab’s (Adansonia gregorii) flowering and leafing period. Madeleine Brockman • Sean Smith • Maria Harris Received: 20 May 2013 / Accepted: 29 May 2013 Subject Editor: Christopher Jones, Manuscript Editor: Susan Barker Abstract The genus Adansonia commonly known as the boab, undergoes seasonal leaf and flower growth and removal. The aim of this paper was to investigate whether the trees change the start time and length of these phenophases in response to rainfall in the previous and present seasons to allow proper management of water. It was expected that a drier wet season will cause the boabs in the next season to grow new leaves and flower sooner and that a lower amount of rainfall in a present wet season will cause flowers and leaves to be present on the trees for a shorter period of time. ClimateWatch data, which uses the reports of ‘citizen scientists’ to plot the timing and duration of phases in the boab lifestyle was analysed to determine the relationship in Australia while a separate study on African boabs was used to analyse African data. The results did not show any distinct change in the timing of any phenophase, though the conclusions were hampered by incomplete, brief and sometimes contradictory data. Keywords – boab, phenology, rainfall, Adansonia, leafing, flowering, climate change 1 Introduction Phenology is the influence of seasonal changes on the annual events of flora and fauna, for example flowering times, migration and mating. A study of phenology through data sets can lead to an evaluation of the effect of climate change on a particular species and the effect that this species has within its community and food web, and is essential to present day problems such as conservation of threatened species. Climate change is a variation in weather patterns over time, changes including temperature, rainfall, solar radiation, and oceanic processes or circulation. While these changes are caused in part by natural cycles, the speed at which some of the changes have escalated is mostly 12 agreed to be caused by human activity, i.e. the greenhouse effect (IPCC 2007).The impact that climate change is having on rainfall is more unpredictable than most other weather patterns as the trends in rainfall include changes in distribution as well as abundance (Trenberth 1998). The increased global temperature means that the atmosphere is able to hold more moisture, and the increase of infrared radiation on the Earth’s surface contributes to evaporating surface moisture, and combined this means that actual moisture within the atmosphere should increase. While this means that more rain should fall in certain weather systems, the causal basis of the changing pattern is still not fully understood (Trenberth 1998). Rainfall trends in the Northern Territory of Australia have slightly increased from 1900 to 2012 (Australian Bureau of Meteorology 2013) and have slightly decreased in Zimbabwe from 1900 to 2000 (Doyle 2007). The Australian and African Boab, Adansonia gregorii and A. digitata respectively, are part of a genus with eight extant species that rely upon the timing of rainfall events to survive in their environment. This report analyses the extent to which rainfall events influence phenology in order to make predictions about what effect climate change will have on the trees in the future. For the purposes of having a large enough bank of data any difference between species which would affect the timing of phenological events has been deemed negligible, especially considering that the Australian species is theorised either to have been the same direct ancestor species when the continents were joined or else, brought to Australia from Africa through human migration (Bowman 1997). The boab is categorised as a deciduous tree, losing its leaves in the dry season and producing new growth at the start of the wet season (note that the wet season in the tropic areas runs from around November to April, and the wet season in Perth occurs from June to August). Deciduous growth patterns have emerged in plants that evolved in climates where plants must live without water or in near drought conditions for several months a year. Leaves have many small openings called stomata and they facilitate gas exchange for photosynthesis. Through transpiration these openings (stomatal pores) stay saturated with water and as wind blows past the water vapour slowly diffuses away. Thus even with the ability to open and close the pores throughout the day, some water is always being passively lost. Boab trees are characterised by a large, swollen, shiny trunk with a disproportionally large circumference to height and large taproots for absorbing water in the lowest levels in the water table. The trees do an excellent job of collecting and storing water to safeguard against drought and provide the water to create new leaves, or for leaf flushing (Chapotin et al. 2006). Boab’s survive during the dry season on the vast amounts of stored water in their swollen trunks, and photosynthesise from the trunk cells, until the next wet season. This adaption must happen correctly during the critical months for initial leaf-flush (Sanchez et al. 2011), perhaps to maximise the efficiency of photosynthesis during the short and highly variable wet seasons (Chapotin et al. 2006). The initial flushed leaves do not actually begin to respire until the onset of rain but are present so as to be ready for the start of the wet season (Sanchez et al. 2011). The 13 phenological event of leaf flushing can thus be hypothesised to be determined by the previous wet seasons’ total rainfall as, in theory, the tree will wait until its water stores are almost depleted to flush leaves. The timing of flowering is also deemed to be influenced by the onset of rainfall as it requires a ready supply of water and the animal vectors for transmission of boab pollen are becoming abundant during this same period. For the trees to have flowers outside of this period would create a trophic mismatch (Mitchell 2013). This report will be looking at data from ClimateWatch (www.climatewatch.org.au) that was collected by citizen scientists. The data will be analysed to determine when and how long the two phenophases of interest occur. The ClimateWatch data are observations of recently replanted baobabs in Kings Park, Perth and several specimens in the Kimberleys, Western Australia. The data will be compared with those from a previous study that included 126 African Boabs in Zimbabwe (Swanepoel, 1993). This investigation seeks to evaluate the relationship between the amount of rainfall as a determining factor for the timing of the new leafing and flowering events. It is an expectation that a drier wet season from one period will cause the boabs to grow new leaves sooner in the next and that a lower amount of rainfall in the present season will cause them to be present on the trees for a shorter period of time. 2 Materials and Methods Data collected from Climate Watch (2013) consisted of sightings of the Australian Boab tree by citizens that were then uploaded to the Climate Watch website. The information uploaded included the location of the boab and what phenophase was seen. Options people could choose were various stages in the flowering, leafing, and seed presence (ClimateWatch 2013). Climate Watch data was provided in Microsoft Excel format. We edited the data to remove very inconsistent sightings that were outnumbered by the exact opposite of other sightings around it. A table was constructed to show the flowering and leafing periods of the boab tree. This made it clear that the boab tree has a distinct phenophase, which slightly differs between years. The Australian Bureau of Meteorology (www.bom.gov.au) enabled access to the temperature and rainfall data for Perth, where most sightings were made. An average monthly temperature across the range of the ClimateWatch dataset was determined. This allowed a connection to be seen between the phenophases of the Australian Boab with the rainfall (Fig 1) and temperature (Fig 2) of Perth (Australian Bureau of Meteorology, 2013). Researching the boab trees in Africa led to information being gathered on the phenophases of this tree. All data for the rainfall and seasonal events for the African Boab are presented as described by Swanepoel (1993). A comparison between the boab phenophases in Africa and Australia was conducted. 14 3 Results Over 90% of the ClimateWatch data was on the boab trees found in Kings Park, Perth. These sightings showed that the Australian Boab leafing began in August of 2011, and September of 2012. The flowering of this species started in October of 2011 and September of 2012. This is shown in Table 1. It can be seen that the Australian Boab responded to the temperature and rainfall of the climate, leafing and flowering when the temperature increased after a large quantity of rain as shown in Figs. 1 and 2. Table 1 ClimateWatch data has been analysed to show the different phenophases of the Australian Boab observed from August of 2011 until March of 2013 (ClimateWatch 2013) Year (month/year) Start of Leafing End of Leafing Leafing period Start of Flowering End of Flowering Flowering period 2011-12 8/11 5/12 9 months 10/11 5/12 7 months 2012-2013 9/12 After 3/13 >6 months 9/12 After 3/13 >6 months Fig. 1 The average rainfall received in Metropolitan Perth during the years of 2010, 2011 and 2012. Distinct high and low rain periods can be observed. Data from Australian Bureau of Meteorology (2013) 15 Fig. 2 The average temperature Metropolitan Perth received during the period of 2010 to 2012 (Australian Bureau of Meteorology 2013). This graph shows a close relationship to the rainfall received during this period. Table 2 The data for African Boabs in Zimbabwe, (Swanepoel 1993). Leaf loss and rainfall from 1983 – 1986 are shown. Date of leaf loss Rainfall total of previous season Rainfall of current season October 1983 13/5/1984 375 mm 399 mm 7 October 1984 8/7/1985 399 mm 883 mm 9 November 1985 3/7/1986 883 mm 891mm 8 October 1986 27/5/1987 891 mm 363 mm 7 Date of leaf flush (more than 50% of trees) Time trees spent with leaves (months) 4 Discussion Considering the data from ClimateWatch (2013) and the previous research in Africa (Swanepoel 1993), the hypothesis that the length and timing of the leafing and flowering period of boabs is directly correspondent to the rainfall is inconclusively supported. In years of greater rainfall, the boab was shown to both have a longer leafing and flowering period, therefore in part supporting the hypothesis. However, the amount of rainfall in the previous year had no detectable influence on the timing of the leafing and flowering period, in part disproving the hypothesis. This conclusion however, is inconclusive on account of the limitations of the data available. Furthermore, there are no previous studies that support our conclusions historically apart from the data obtained in Africa (Swanepoel 1993), so no comparison of data sets can be made to verify the reliability of the data that are available. 16 The quality and reliability of the data is affected by several data entries in the ClimateWatch website that are incomplete or in direct contradiction to the rest of the data set, such as the boab having no leaves in the middle of the leafing period. The reliability of the data from Africa (Swanepoel 1993) was also affected by additional environmental disruptions, as during the study of the African Boabs, elephants damaged many of the trees. It is unknown how this influenced the trees’ flowering and leafing time, or whether it influenced them at all. The large boab in Perth was transplanted from the Kimberleys in 2008, at which time it experienced a complete shift in weather pattern from the timing of the wet and dry seasons, from tropical to Mediterranean climates. Though this happened three years before the data from ClimateWatch was collected, the influence of this traumatising change could have affected results for the flowering and leaf growth of that particular tree. The data from ClimateWatch only covers two reproductive seasons of the Australian Boab, which is an inadequate amount of time to properly analyse and find trends relating to anychange in phenology. Data was generalised for our study, and as a result of this the exact timing of the leafing and flowering could not be obtained, severely limiting the accuracy of our conclusions. The African data (Swanepoel 1993) covers only four reproductive seasons of the boab, and while a co-relationship is apparent, trends cannot be attributed solely to rainfall, as there are other factors that may influence this correlation. Other environmental factors that might influence the phenology of boabs include temperature (Table 1) which is known to have an effect on seasonal events of other native Australian species (Gallagher et al. 2009). While the overall temperature of 2011 in Australia was lower than in 2012 and the leafing period went for nine months and the flowering period went for seven months compared to the six months for leafing and flowering in 2012, there is not enough data to determine a trend. In comparison there is a clear relation to the date of leaf loss of the African Boab and the temperature and rainfall of that year; higher temperatures and lower rainfall correlated with leaf drop earlier in the year (Swanepoel 1993). From analysis of the ClimateWatch data, it can be determined that lower rainfall correlated with the leafing and flowering period being shorter in duration (Fig. 1 and Table 1). Further studies with a larger and more reliable data set are recommended to determine the strength of the relationships between temperature, rainfall and phenology of the Australian Boab. The expected trend of the length of the leafing and flowering period could be predicted by an evaluation of the rainfall trends of a particular area. From this can be extrapolated a prediction of the effects on ecosystems of which they are a part and the fauna that rely on the boab as a food source, for example hawkmoths in Australia (Bowman 1997). The relationship between the boab and animals that rely on them will be affected if the length of the leafing and flowering times of the boab change. The boab will then be further affected as animals that are vectors for pollen and fertilisation change their feeding habits. From this it can be inferred that a change in rainfall may have a massive effect on the whole ecosystem, and that the different rainfall levels in the Mediterranean (Perth) and tropical (Kimberleys and Zimbabwe) climates will affect how the boab interacts with its ecosystem. 17 It is because of this predicted relationship that the boab is an important indicator species for climate change. However, because of the unreliability of the ClimateWatch data set, further research and study must be conducted in order to better understand the effect of climate change on boabs as well as the effect of climate change on Australia’s ecosystems and biodiversity. While the temperature cannot accurately be said to affect the times or duration of leafing and flowering of the boab, and the previous seasons’ rainfall total can be seen to have no affect on the commencement time of the leafing and flowering, it can be seen that the rainfall of the present season can affect the duration of the leafing and flowering periods of the boab. Acknowledgements We would like to acknowledge ClimateWatch and C.M. Swanepoel for providing the data on boabs that was used in this study. References Australian Bureau of Meterology, 2013, Available from: <http://www.bom.gov.au/climate/> Accessed on 20 May 2013 Bowman D, 1997, ‘Observations on the demography of the Australian Boab (Adansonia gibbosa) in the Northwest of the Northern Territory, Australia’, Australian Journal of Botany, vol. 45, pp. 893-904 Chapotin S, Razanameharizaka J & Holbrook NM, 2006, ‘Baobab trees (Adansonia) in Madagascar use stored water to flush new leaves but not to support stomatal opening before the rainy season‘, New Phytologist, vol. 169, pp. 549-559 ClimateWatch, 2013, Available from: <http://www.climatewatch.org.au> Accessed 20 May 2013 Doyle A, 2007, ‘Africa “forgotten continent” in climate fight’. Available from: <http://www.appinsys.com/GlobalWarming/ReutersAfrica.htm> Accessed on 16 May 2013 Gallagher RV, Hughes L & Leishman MR, 2009, ‘Phenological trends among Australian alpine species: using herbarium records to identify climate-change indicators‘, Australian Journal of Botany, vol. 57, no. 1, pp. 1-9 IPCC, 2007, ‘IPCC Fourth Assesssment Report: Climate Change 2007’. IPCC, Geneva, Switzerland: Intergovermental Panel on Climate Change. Mitchell N, 2013, ‘Resource use and Phenology’, lecture notes distributed in BIOL1130 at The University of Western Australia, Crawley on 18 March 2013 Sanchez A, Osborne P & Haq N, 2011, ‘Climate change and the African baobab (Adansonia digitata L.): the need for better conservation strategies‘, African Journal of Ecology, vol. 49, pp. 234-245 Swanepoel CM, 1993, ‘Baobab phenology and growth in the Zambezi Valley, Zimbabwe’, African Journal of Ecology, vol. 31, pp. 84-86 Trenberth K, 1998, ‘Atmospheric moisture residence times and cycling: implications for rainfall rates and climate change’, Climatic Change, vol. 39, pp. 667-694 18