Lack of aggression and apparent altruism towards intruders in a primitive termite.

Ethology, Publication
Co-authoring for a publication in Royal Society Open Science.

 

The following journal article was written and published online in 2016 for which I am proud to be named as a co-author for the first time. This project was based on methods of Pterotermes occidentis husbandry, marking, and observational procedure that I developed as part of my BSc dissertation in Zoology (A cooperative function of allogrooming in a primitive drywood termite species) at the University of Exeter in 2012-13.

 

Authors

Feargus Cooney*, Emma I. K. Vitikainen*, Harry H. Marshall*, Wilmie van Rooyen*, Robert L. Smith**, Michael A. Cant* and Nicole Goodey*.

 *Centre for Ecology and Conservation, University of Exeter, Penryn Campus, Cornwall, TR10 9EZ, UK
**Department of Entomology, University of Arizona, Forbes 410, Tucson, AZ 85721-0036, USA

 

Abstract

In eusocial insects, the ability to discriminate nest-mates from non-nest-mates is widespread and ensures that altruistic actions are directed towards kin and antagonistic actions are directed towards non-relatives. Most tests of nestmate recognition have focused on hymenopterans, and suggest that cooperation typically evolves in tandem with strong antagonism towards  on-nest-mates. Here, we present evidence from a phylogenetically and behaviourally basal termite species that workers  discriminate members of foreign colonies. However, contrary to our expectations, foreign intruders were the recipients of  ore rather than less cooperative behaviour and were not subjected to elevated aggression. We suggest that relationships  between groups may be much more peaceable in basal termites compared with eusocial hymenoptera, owing to energetic and temporal constraints on colony growth, and the reduced incentive that totipotent workers (who may inherit breeding status) have to contribute to self-sacrificial intergroup conflict.

 

PDF of full article

 

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Factors affecting relative mite density differ for male and female Greater Horseshoe bats (Rhinolophus ferrumequinum) from Southwest England.

Article, Ecology & Conservation, Natural History, R Statistics
A report of data analysed using R Software for Environmental Statistics, with a specification requiring publication writing style and a 2500 word limit. 

 

Abstract

There is much aggregation of parasites in nature but the factors influencing ectoparasite variation in mammals and how this affects populations are unclear due to costly compensatory behaviours performed, such as grooming. Bat research is lacking due to their sensitivity and protection. This study uses body mass, forearm length and ectoparasite count data collected over decades at low-frequency during the hibernation period of the Greater Horseshoe Bat, to elucidate the different factors affecting average relative mite density (RMD) in males and females of high and low reproductive condition. On average, females were larger than males, carrying more mites, with females of high reproductive condition carrying significantly more than males and non-reproductive females, suggesting lowered immunocompetence or a grooming/reproduction trade-off. Using the Akaike’s Information Criterion and significance of Confidence Intervals, Ordinal Logistic Regression models, show that differing factors are likely to determine RMD for male and female Greater Horseshoe bats with possible implications for their conservation.

Key words: Ectoparasite, variation, reproductive, condition, trade-off

Introduction

Parasites are known to be heterogenetic in mammals (Wilson et al. 2001) but information about the variation in magnitude and probability of infestation within bat populations is lacking (Lucan 2006; Frank et al. 2015; Orlova et al. 2015).Ectoparasite infestation is likely to depend on exposure level and immunocompetence (Hart 1992; Luguterah and Lawer 2015) and females are often more heavily infected than males (Zahn and Rupp 2004; Patterson, Dick and Dittma 2008; Presley and Willig 2008) due to fundamental life-history differences such as sexual size-dimorphism or age differences (Stebbings 1966), and behaviour such as aggregation by reproductive females not exhibited by males (Williams and Findley 1979; Ransome 1991). Reproductive condition and related hormones can also have an effect on overall bat parasite load (Christe, Arlettaz and Vogel 2000).

Bat are rare and highly protected in the UK, (Joint Nature Conservation Committee 2014; The Bat Conservation Trust 2016) carrying a variety of ectoparasites including mites (Sachanowicz, Kristofik and Ciechanowski 2014; Frank et al. 2015) which need contact between bats for transmission (Reckhart and Kerth 2009) The understanding of bats is of ecological importance as they contribute to essential ecosystem services such as insect control and pollination (Kunz  et al. 2011; Ghanem and Voigt 2012; Wanger 2014), and this study aims to investigate variation in average parasitic mite load per individual (relative mite density) in the Greater Horseshoe bat, (Rhinolophus ferrumequinum) using data collected over 34 years from 39 locations, via low-disturbance methods, during autumn and winter months.

In the UK, populations of R. ferrumequinum are confined to southwest England (The Bat Conservation Trust 2016). This species is particularly sensitive to site disturbance (Hutson, Mickleburgh and Racey 2001) but can be handled during torpor (e.g. Park, Jones and Ransome 2000)  in hibernacula over  autumn and winter Similarly to other bat species females are larger and likely have higher relative mite density (RMD) than males.

The Body Condition Index (BCI), a ratio calculated by dividing body mass by forearm length, has been used to investigate ectoparasite load (Speakman and Racey 1986; Lucan 2006; Sharifi et al. 2013; Postawa and Szubert-Kruszyriska 2014) and  preliminary analyses, using scatterplots with linear regression lines and the Spearman’s rank correlation coefficients for the data of  this study, demonstrated that there is no significant correlation between RMD and body condition for R. ferrumequinum  males or females (Appendix 1: Table 1, Fig. 1), supporting similar findings in other bat species (Zahn and Rupp 2004; Lucan 2006; Sharifi et al. 2013, Postawa and Furman 2014;Postawa and Szubert-Kruszyriska 2014)

Body mass, forearm length, and RMD were compared for high and low reproductive condition males and females (indicated by visibility of false nipples in females and testes in males) and regression models were created to explain and predict RMD variation for the sample population as a whole, as well as for male and female data separately, to reveal potential differences in factors determining RMD between males and females.

First, greater body mass, forearm length and RMD was predicted for high reproductive condition (RC) females than for both females of low RC and all males (Sharifi et al. 2013). This is hypothesised to be due to the dynamics between parasite and host that take place within summer colonial roosts of adult females and some juveniles, but which adult males attend rarely and only until females give birth (Piksa et al. 2014). The higher density individuals within a roosting colony can have increases probabilities of horizontal and vertical ectoparasite transmission (Patterson, Dick and Dittmar 2008; Presley and Willig 2008).

RC in males and females is associated with age and body mass (Ward et al., 2014) and parasitic mites may have adapted their reproductive cycle to that of their host (Christe, Arlettaz and Vogel 2000; Lourenco and Palmeirim 2008). High RC (possibly pregnant) females may have a greater RMD than low RC, possibly juvenile, females during the autumn and winter, until the time of birth (summer) when parasites are thought to move onto male and female juveniles in the roost (Christe, Arlettaz and Vogel 2000). Therefore the second prediction of this study is that males of lower RC would have a higher RMD, but lower body mass and forearm length than both higher RC males and low RC females.

Finally, due to the possibility of different underlying causal mechanisms (Ward et al. 2014) influencing their parasite load (Lucan 2006), female RMD variation is predicted to be more dependent on RC than body mass or forearm length, while male RMD variation is predicted to be more dependent on body mass than on RC or forearm length.

Materials and Methods

a. Data Collection

R. ferrumequinum were captured while in torpor, weighed (g), sexed, aged by rating the ossification of joints (Kunz 1988) from 0-4, forearm length measured (mm) and number of wing mites and tail mites counted. The visibility of false nipples was recorded for females, the absence of which indicating non-reproductive condition (Dietz and Dietz 2007). For males, degree of testicular visibility was recorded, and larger or smaller testicle size can be an indicator of higher or lower spermatogenesis, respectively, during autumn and winter (Haarsma 2008).  Bats were released by placement back on the cave wall in a suitable position. Hibernacula temperature, outside temperature and humidity were recorded at least once for most of the sites, except four which contributed very little data in total.

Data was collected between 1976 and 2010 from approximately 39 locations in Southwest England at varying frequencies (Wiltshire Bat Group 2015). Hibernacula at each site were usually visited, between November and April but in total, the majority of data was collected from 7 main locations with most data being collected between 2002 and 2010. Thus, spatial and population dependence is expected of the data. This low-frequency sampling by volunteering members of the Wiltshire bat group, and handling of bats during torpor  (e.g. Park, Jones and Ransome 2000) under the supervision of a licenced bat handler, likely limited disruption.

b. Data Selection and Manipulation

Due to the large number of data entries for which two or more variables were unrecorded, gaps in the data were filled in using the mean of the recorded values (assuming no trend in the data in order to prevent bias), resulting in 1293 males and 1236 female data points for each recorded variable. This enabled statistical analyses without eliminating large parts of useful data.

New variables were systematically created from the raw recorded data. Male testes visibility, originally ranked from 0-4, was categorised into males with more regressed testes (visibility 0, 1 and half of 2) and males with more pronounced testes (visibility 3, 4 and the other half of 2). These categories, along with visibility of false nipples in females, were then given a rank of either 0, representing low RC (males with more regressed testes and females without visible false nipples), or 1, representing high RC (males with more pronounced testes and females with visible false nipples).

RMD was calculated, as the number of tail mites added to wing mites per bat, and since these data contained a high frequency of zero values, they were ranked into 8 ordinal groups (rank 1 = 0-2 mites/bat, rank 2 = 3-5 mites/bat, rank 3 = 6-8 mites/bat, rank 4 = 9-11 mites/bat, rank 5 = 12-14 mites/bat, rank 6 = 15-17 mites/bat, rank 7 = 18-20 mites/bat and rank 8 = 21 or more mites/bat) in order to avoid problems caused by high frequencies of zero values during statistical analyses.

c. Data Analysis

Effects of body mass, forearm length and RC on RMD were investigated using the statistical analysis software R (R Core Team, 2015), with all tests carried out at a 95% confidence interval. Before doing analyses, the data was explored, assessing outliers, distribution normality and homoscedasticity. Six extreme high and low outliers for body mass and forearm length data were removed as these were possibly caused by measurement error. Extreme outliers for RMD were all larger than the average and were not removed as individuals in natural animal populations can experience extreme infestation (e.g. Boulinier, Ives and Danchin 1996; Pierce et al. 2014; Frank et al. 2015).

Since the data for RMD was greatly right skewed, Kruskall-Wallis and Mann-Whitney U tests were done to investigate the differences in ranked RMD between males and females, and between RC groups (Kowalski, 1972). Body mass and forearm length data were found to be nearly normally distributed with similar homogeneity of variances, leading to the use of a one-way ANOVA and two-sample unpaired Student’s t-Tests to examine differences in the two variables between males and females, and between the RC groups.

Ordinal Logistic Regression (OLR) models were fitted using the Proportional Odds Regression function and MASS package in R (Venables and Ripley 2002), to explore the causal relationship between the ordinal dependent variable, RMD and the covariates (predictor variables) body mass, forearm length and RC on variation in RMD. Nine OLR models using the combined male and female data, male-only and female-only data were run and the Aike Information Criteria (AIC), Confidence Intervals (CI) and Odds Ratios were used to select an appropriate model that could explain the variation in RMD for each set of data.

To validate the models, evaluation of the Proportional Odds Assumption was carried out by running a series of binary logistic regressions and assessing the equality of the difference in coefficients of the logits for every outcome of the predictor variable, at each level of the dependent variable.  Finally, the predicted probabilities for the new models, of a given dependent variable level being the case, at every given predictor variable level was plotted using the packages reshape2 (Wickham 2007) and ggplot2 (Wickham 2009) and compared to graphs of actual data in order to assess the models’ effectiveness.

ALL R CODE SCRIPTS

Results

(For all statistical tests except OLR, results were significant unless otherwise stated)

a. Abiotic Factors and Bat Age

Outside temperature ranged from 0-18°C (8.5°C average). Hibernacula temperature ranges 0-18°C (9.1°C average), and humidity ranges 9.6-100% (86.1% average). Bat joint ossification ratings ranged 0-4 but the average was 3.

b. RMD Variation

Females had 1.14 times (Fig. 2) greater average RMD than males (Appendix 2, Table Set 2.a). Females of high RC had 1.063 times significantly greater RMD than females of low RC. Males of lower RC had 1.071 times greater average RMD than males of higher RC but this difference was not significant. High RC females had greater average RMD than all males while there was no significant difference between low RC females and males of either RC (Appendix 3,Table 3.b) , supporting the trend in Fig. 2.

c. Body Mass Variation

Female bats had 1.050 times (Fig.3) greater average body mass than males (Appendix 2, Table 2.b). High RC females had 1.063 times greater average body mass than low RC females, and males of both higher and lower RC. Higher RC males had 1.062 times significantly greater average body mass than lower RC males. There was no significant difference in body mass between low RC females and higher RC males but low RC females had significantly greater average body mass than lower RC males (Appendix 3, Table 4.b). These results support the trend in Fig. 3.

 

 

d. Forearm Length Variation

On average, female bats had 1.017 times (Fig. 4) longer forearms than males (Appendix2, Table 2.b). High RC females had 1.003 times greater average forearm length than low RC females and males of both higher and lower RC (as did females of lower RC). Higher RC males had 1.006 times greater forearm length than lower RC males (Appendix 3, Table 4.c). These results support the trend in Fig.4.

e. Ordinal Logistic Regression modelling

Nine OLR models were created with each predictor variable in turn, using combined, as well as male-only and female-only data (Appendix 4, Table 5). The CI was significant for models using 1. body mass and RC for combined data, 2. body mass for male-only data, and 3) RC and forearm length for female-only data.  The AIC and Residual Deviance for the models that did not have significant CI was also relatively high. In the female-only data, forearm length Odds Ratio showed an inverse relationship with RMD compared to the Odds Ratios for the other significant variables. The predictor variables of these significant models were used to fit three OLR models, M1 (combined data), M2 (male) and M3 (female), that may predict the variation in RMD of R. ferrumequinum (Appendix 5, Table 6) for the sample population.

 

For model validation, the Proportional Odds Assumption was found to be violated for RC in M1 but not for Body Mass (Appendix 6, Table 7). It was not violated in M2 (Appendix 6, Table 8), and was violated for Forearm Length in M3 but not for RC (Appendix 6, Table 9). The predicted probabilities of a given level of the dependent variable being the case, at any given level of each predictor variable, were then plotted for each model and compared to graphs of actual data (Fig.5, 6, and 7). The models were found to effectively predict the change in RMD in relation to 1. Body Mass and RC for the combined data, 2. mass in the male data and 3.forearm length and reproductive condition in the female data .

Model 1 used Body Mass (g) and RC (0=lower, 1=higher) to explain ranked RMD (levels 1-8). This model had the highest AIC, with the effect of RC being found not significant. The Body Mass variable had an odds ratio of 1.06: the odds for a higher outcome in RMD is 1.06 times greater at any higher value of Body Mass compared to the next value down, given that all other variables stay constant (Appendix 5, Table 6). Model 2 used only Body Mass to explain ranked RMD in male bats. This was the model with the lowest AIC, with the same general outcome as for Model 1(Fig. 5.), but with a greater Odds Ratio of 1.09 (Appendix 5, Table 6). Model 3 used RC and Forearm Length (mm) to explain ranked RMD in female bats and also had a relatively low AIC, with the highest Odds Ratio for RC of 1.57 and the lowest odds ratio for forearm length at 0.84, meaning the odds for a higher outcome in RMD is 1.57 times greater at higher RC than at low RC, and approximately 1.2 times greater at a lower forearm length compared to the next value up, given that all other variables stay constant (Appendix 5, Table 6).

Discussion

Ectoparasite load can carry implications for reproduction and survivorship (Giorgi et al. 2001; Simon et al. 2004; Hawlena, Abramsky and Krasnow 2006). Direct impact may occur through resource consumption (Hawlena, Abramsky, Krasnov 2006) and imposing immunocompetence costs (Navarro-Gonzalez et al. 2011), as well as indirectly through pathogen transmission, and changes in habitat selection (Reckardt and Kerth 2007).

Grooming behaviour functions as defence against ectoparasite infestation but carries an energetic and time cost (Giorgi et al. 2001; Godinho et al. 2013) that may also impact the ability of an animal to rest, forage, defend its territory or mate, reproduce and care for young (Giorgi et al. 2001). This energetic cost may also vary according to differences in the cost that different parasite species draw from hosts (Godinho et al. 2013).

For this study of R. ferrumequinum during autumn and winter in southwest England, average RMD was greater in high RC females than any other group, while there was no significant RMD difference between low RC females and any males, supported by other studies (Christe et al. 2007; Encarnacao, Baulechner and Bekcer 2012; Sundari et al. 2012).

Grooming behaviour may be energetically and time restricted in reproductive females and inefficient in low RC individuals that are likely to be juveniles (McLean and Speakman 1997; Viljoen et al. 2011; Encarnacao, Baulechner and Bekcer 2012). Reproductive females may also have reduced immunocompetence due to hormonal changes (Christe et al. 2000) or to a resource allocation trade-off for reproduction (Dzal and Bringham 2013). In addition, reproductive females tend to live in close colonies in maternity roosts for part of the year, often with some juveniles, while non-reproductive females and males roost solitarily (Ransome 1991) leading to a greater probability of parasite transmission within the reproductive female population (Christe, Arlettaz & Vogel 2000; Patterson, Dick and Dittmar 2008).

Modelling found that high RC females are more  likely to have a higher level of mite infestation than low RC females (and all males) but longer female forearms mean lower probability of high-level mite infestation and vice versa (Fig. 7). Greater body mass may mean lower probability of low-level mite infestation and higher probability of higher-level infestation for all bats (Fig. 5) as is the case for males separately  (Fig. 6) but not for females separately. Possible reasons include higher mass providing more surface area and more resources for mites to inhabit (Viljoen et al. 2011) and less energy spent on costly grooming when larger individuals are able to carry the cost of infestation better than small individuals (Giorgi et al. 2001).

Differences in body mass, forearm length and RMD between the study groups were extremely small, as were the predicted increases or decreases in RMD, and there is a general need for future study of factors affecting on  mite infection intensity (average mites per infected bat) and prevalence (percentage of infested bats).

In general, ectoparasite load does not affect overall bat health ( this study’s Appendix 1: Table 1, Fig. 1; Zahn and Rupp 2004; Lucan 2006; Sharifi et al. 2008; Postawa and Szubert-Kruszyriska 2014) but at times of more intense demand on resources, even a moderate parasite load may affect survival. Fluctuations in climate, lack of suitable roosts and decreased food availability such as those faced by bats in the UK (Ransome 1968; Hutson, Mickleburgh, Racey 2001; The Bat Conservation Trust, 2014) can affect ectoparasite prevalence due to temperature (Chen and Mullins 2008; Lourenco and Palmeirim 2008) and humidity changes (Moyer et al. 2002; Zhang et al. 2010), as well as body mass and immunocompetence (Navarro-Gonzalez et al. 2011; Dlugosz et al. 2014). Heterogeneity of infestation impact due to varying energetic and time demands may carry implications for bat population dynamics and conservation that need further investigation over the course of all seasons (Lourenco and Palmeirim 2008; Sharifi et al. 2008).

 

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Appendix 1.

Preliminary finding for the effects of an immunity indicator on R. ferrumequinum Relative Mite Density:

 

 

Appendix 2.

Results of statistical tests for differences between male and female R. ferrumequinum.

Appendix 3.

Results of statistical tests for differences within male and female R. ferrumequinum: between individuals with false nipples, without false nipples, and between individuals with larger testes and without larger testes.

 

Appendix 4.

Results of Ordinal Logistic Regression modelling used to select the models which best describe variation in RMD.

 

Appendix 5.

Results of Ordinal Logistic Regression modelling for the three selected models which best describe variation in RMD.

 

Appendix 6.

Predicted linear logits.

 

Classification of the Sengis (Afrotheria, Macroscelididae): challenges in taxonomy affecting conservation prioritisation.

Article, Ecology & Conservation, Natural History
Article on issues in conservation 

 

Adjustments in the classification of many species are driven by, not only new technological and ecological discoveries, but also growing awareness of conservation implications involved with erroneous species classification that may lead to losses in genetically, ecologically, and economically valuable biodiversity (Williams et al., 2012; Richards, Miller and Wallace, 2013; Eldridge, Meek and Johnson, 2013).

Species Concepts

Though classification techniques have developed considerably from the first hierarchical classification of all living things by Aristotle (Hamilton and Wheeler, 2008; Lewis, R., 2015), conflicting ideas about the distinction of organisms are still plentiful, more than 20 species concepts are theorised (Mallet, 1995; Mayden, 1997; Wheeler and Meier, 2000) and there is failure to agree on a common definition of a species (Mitchell, 1993; Bachmann, 2001; Frankham et al., 2012). Of the concepts favoured by scientists, most are either pattern-based, defined via morphology or phylogeny (Mallet, 2009; Filatov et al., 2013) or process-based, defined via reproductive isolation or cohesion (Wirtz, Printzen and Lumbsch, 2008; Lagache et al, 2013; Dirlink et al., 2014), but none are without problems (Hausdof, 2011).

The Morphological Species Concept relies on the distinctiveness of measurable physical characters between groups and similarities within them, but the subjectivity of morphological analyses and potential cryptomorphism of species, poses a problem when groups are morphologically identical but genetically distinct (Funk, Caminer and Ron, 2012) or vice versa (Agrawal, 2001). Many evolutionary geneticists think of species in terms of the Biological Species Concept (BSC), defining a species as an actually or potentially interbreeding natural population, that is reproductively isolated from other similar populations with limited gene flow between them (Wheeler and Meier, 2000; Noor, 2002; Coyne and Orr, 2004). This concept has problems dealing with asexual species, hybridization (Papadopulos et al., 2011) and lack of evidence for reproductive isolation of subject organisms (Wu, 2001).

For the Phylogenetic Species Concept (PSC) molecular sequences are analysed as well as morphology, in order to infer shared derived characters that indicate the smallest monophyletic groups with a single common ancestor (Wheeler and Meier, 2000) and these groups are then classed as species. Taxonomists tend to favour this concept as it gives a clear statistical outcome. However, it is dependent on the extent of molecular and morphological data, the outputs of a phylogenetic analysis are hypothesis based rather than a certainty, and there is particular ambiguity around the degree of differentiation necessary to indicate a separate species using the PSC due to its high degree of precision (Agapow et al., 2004).

Benefits and Risks of  Conservation Prioritisation using Phylogenetic Analysis

It is widely acknowledged that global human-induced species extinction risks are not decreasing (State of Nature Partnership, 2013; Secretariat of the Convention on Biological Diversity, 2014, Regnier et al., 2015), and biodiversity loss is greater than the resources available to restore and protect it (Leader-Williams, Adams and Smith, 2010; Mooney, 2010). In addition, the wide-spread assumption that the majority of species are well known to science has been demonstrated to be a misconception (Smit et al., 2008) and it is suggest that global animal and plant species diversity is underestimated (Vieties et al., 2009; Appeltans et al., 2012). Since large numbers of undiscovered species persist in rapidly declining habitats, many may become extinct before they are discovered, contributing to a decline in biodiversity with implications for ecosystem services (Ceballose and Ehrlich, 2009).

Conservation efforts acknowledge the importance of not only protecting animal populations individually, but also the functional and genetic diversity within and between species (Ceballosa and Ehrlich, 2009; Steele and Pires, 2011; Bennett et al., 2014, Leslie, 2015) in aid of preserving genetic representation of past evolution (Grandcolas, Nattier and Trewick, 2014) and evolutionary potential (Taberlet et al., 2012), as well as present ecological traits. Phylogenetics is often used for species delineation, potentially revealing the true biodiversity of taxa or environments, previously unrecognised (Merces et al., 2015). This can influence the assignment of conservation status because revised species taxonomy due to advances in molecular and morphological techniques such as DNA barcoding (Herbert and Gregory, 2005; DeSalle, 2006) or geometric morphometric methods (Zúniga-Reinoso and Benítez, 2015), can lead to altered species population numbers and range sizes (Funk, Caminer and Ron, 2012).

The elevation of a sub-species to species level (Olivieri, 2007; Pinzo and La Jeunesse, 2011 ) or the description of cryptic species previously undiscovered (Lohman et al., 2010; Feinberg et al., 2014) is often the result of molecular phylogenetic analyses. However, the risk for species classifications that are too narrow when using very precise modern techniques is a concern when such classification is used to assess extinction risk and conservation management that is tailored to the separated taxa. For example, there may be an increased risk of extinction through the unintended loss of genetic variation if threatened species are incorrectly split into several separate units and if their breeding is managed as such (Zachos, 2013).

Prioritising conservation via ranking organisms and ecosystems according to evolutionary distinctiveness and phylogenetic diversity is increasingly found effective (Tucker et al., 2012; Volkamn et al., 2014). As it is based on species ancestry and decent, it often captures similarities among species on multiple levels, revealing phenotypical and ecological differences as well as ancestral ones. This may facilitate more efficient management choices, maximising future conservation returns when ecosystems with great evolutionary diversity, as well as genetic and ecological uniqueness are highlighted (Faith and Richards, 2012; Leslie, 2015).

It is expected that regionally restricted phylogenetic lineages, contribute substantially to the total genetic variation of environments (Rosauer et al., 2009). Such species are often rare, occupying small, fragmented ranges and because this means they may also be most at risk of extinction (Cadotte and Davies, 2010), awareness of their genetic importance is vital (Tucker et al., 2012). Unfortunately, lack of data and incomplete or contentious species records may hinder this type of progress (Collins and Halliday, 2005; Steele and Pires, 2011, Funk, Caminer and Ron, 2012).

 

From Elephant-shrew to Sengi: Species Discoveries and Reclassifications

Changes in classification of taxonomic groups occur frequently (Collins and Halliday, 2005; Williams et al., 2012; Buckley et al., 2014) often due to the discovery of new species as scientific efforts and understanding of taxonomy increase.  The elephant-shrews (order Macroscelididae) are an example of a rare, unique and often isolated, phylogenetic lineage that contributes to the distinctiveness of a range of habitats, and awareness of their genetic importance may contribute to the conservation of the valuable environments they are found in (Rosauer et al., 2009; Cadotte and Davies, 2010; Tucker et al., 2012).

Elephant-shrews are very active, wary and well adapted for sprinting away from natural predators. They are insectivores and omnivores (Kerley, 1995) and species range from less than 50g to 700g in weight (Rathbun, 2009), with the smallest species most recently described (Dumbatcher et al., 2014). Some species are very morphologically distinct and easily identified, while others have similar morphologies and distribution overlap, often leading to misidentification (Tolliver et al. 1989). The majority of elephant-shrew species were described in the 19th century based on morphological and behavioural characteristics. The traditional common name was chosen due their elongated snouts and their assumed relationship with the true shrews (Soricidae). Thus, in a publication by Ernst Heackel in 1866, elephant-shrews were placed in the now abandoned, order Insectivora (Tabuce et al., 2001; Stanhope et al., 1998).

The discovery of new fossil evidence means that elephant-shrews are currently accepted as order Macroscelidea (Butler, 1956; Patterson, 1965) and they possess a combination of traits that are unique (Rathbun, 2009): an elongated proboscis-like snout used to forage, saltatorial running, no or limited use of nests, social monogamy, small litters of precocial young and absence of maternal care of neonates (Rathbun, 2009). These are traits that have individually also been associated with small antelopes or anteaters but it was soon realised that elephant-shrews lack close relation to any other living mammals. There have been attempts at linking them to various groups (Rathbun, 1979; Butler, 1995) such as the order Lagomorpha (rabbits, hares and pikas) due to hind leg physiology (Evans, 1942), ungulates due to morphological phylogenetic evidence (Zack et al., 2005), and tree shrews (order Scandentia), a relative of the primates (Simons, Holroyd and Brown, 1991).

Extant and fossil Macroscelidea are all endemic to Africa and analyses of evolutionary relationships using morphological (Oduor-Okeloa, Katemaa and Carterb, 2004; Woodall, 1995), and molecular (Robinson et al., 2004; Svartman et al., 2004) techniques have now strongly, but not without objection (Zack et al., 2005), confirmed the place of Macroscelidea within Afrotheria, along with the elephants (order Proboscidea), sea cows (Sirenia), hyraxes (Hyracoidea), aardvark (Tubulidentata), and golden-moles and tenrecs (Afrosoricida), all of which were previously grouped either with the ungulates or insectivores (Hedges, 2001). Afrotheria is thought to be a distinct ancient monophyletic African radiation, evolved when the continent was isolated from others through plate tectonics (Springer et al., 1997) and its extant clades are not closely related to any other group of mammals (Stanhope, 1998; Staythorpe et al., 1998; van Dijk et al., 2001; Carter et al., 2004; Seiffert, 2007;  Tabuce et al., 2007; Asher and Lehmann, 2008).

The acceptance of the long-suspected super-cohort Afrotheria , and the placement of elephant shrews within it, has drawn both scientific interest (for example, Poulakakis and Stamatakis, 2010) and valuable publicity (‘Insect Hunters’, 2002; ‘Under Open Skies’, 2014) to this unique taxon. In addition, with the progression of molecular identification techniques, new species of elephant shrew are being described, adding to the existing record of species diversity for the habitats in which they are found.

In 1968, Cobert and Hanks investigated the phenotypic relationships among the genera of Macroscelidea based on morphological differences. They identified 2 subfamilies consisting of 4 genera with 14 species in total: the giant, forest-dwelling Rhynchocyoninae (Rhynchoncyon, 3 species) and the soft-furred Macroscelidinae (Elephantulus, 9 species; Petrodromus, 1 species; Macroscelides, 1 species).  Cobert (1971) then described Elephantulus fuscus, raising it to species level from being a subspecies of E. brachyrhynchus. There have been only 22 documented locations for E. fuscus, with a restricted distribution to Malawi, Mozambique and Zimbabwe, and the lack of current habitat and behavioural records for this species means its conservation status is unclear (Rathbun, 2015).

In order to distance Macroscelidea from their mistaken relations, the true shrews, Jonathan Kingdom (1997) suggested the common name “sengi” (a term derived from central African languages) that is increasing in popularity. Five more species have been described since then, often using molecular phylogenetic techniques to resolve minor and sometimes cryptic, differences among the many described forms.

In 2005, Rhynchocyon udzungwesis was observed in the forested Udzungwa Mountains, Tanzania, and declared a new species based on 49 camera trap images, 40 sightings and 5 specimens. It is the largest of all the sengis and is distinguished by unique phenotypic features and allopatric distribution (Rovero et al., 2008). Rovero et al. acknowledge the fact that craniometrics data for this genus is lacking, making a full comparison between new and long-known species very difficult.

Elephantulus pilicaudus was newly distinguished from the phenotypically similar and sympatric E. rupestris and E. edwardii. by Smit et al. (2008) on the basis of strong, morphological, mitochondrial and nuclear DNA, and comparative cytogenetic evidence, from 17 specimens of the new species compared to 25 specimens of E. rupestris and E. edwardii. Smit et al. (2008) also provides a scheme of identification of the distinctive phenotypic characters of E. pilicaudus.

What was thought to be two subspecies of Macroscelides, were both elevated to species level, M. proboscideus (the “Karoo round-eared sengi”)and M. flavicaudatus (the “Namib round-eared sengi”), by Dumbatcher et al. (2012) based on genetic and morphological data, near sympatry with no genetic evidence of gene flow, and differences in habitat use.

Finally Macroscelides micus (Etendeka round-eared sengi) was discovered by Dumbatcher et al. (2014) when an unusual specimen was retrieved from remote Namibia while studying Macroscelides systematics and taxonomy, using phenotypical and DNA evidence. With notable divergence from other Macroscelides at every locus examined and very easily distinguishable morphological features, M. micus is the smallest of the sengis at less than 30g, and appears reproductively isolated. Subsequently, 19 living species are currently described (Rathbun, 2015) in two subfamilies with 4 genera: the giant sengis, Rynchocyoninae (Rhynchocyon, 4 species) and the soft-furred sengis, Macroscelidinae (Petrodromus, monspecific; Macroscelides, 3 species; Elephantulus, 11 species).

Relevance of Species Delimitation to Sengi Conservation

Having been placed in the super-cohort Afrotheria, strong molecular phylogenetic evidence has suggested an unusual ancestry and this information could make sengis a priority for conservation (Kuntner, May-Collado and Agnarsson, 2011). All sengi species are rare so their vulnerability to habitat loss and fragmentation due to anthropogenic effects is concerning , and those found at relatively low densities in forest ecosystems, namely all four species of giant sengis, sub-family Rynchocyoninae, are considered at risk (Nicoll and Rathbun, 1990). The 2013 IUCN Red List of mammals shows R. chrysopygus (the golden-rumped sengi) as “endangered”, R. petersi (the black-and-rufous sengi) and R. udzungwensis (the gray-faced sengi) as “vulnerable”, and R. cirnei (the checkered sengi) as “threatened”. Three species of Elephantulus are listed as “data deficient” and the rest are considered “least concern” (Rathbun, 2015). Knowing and communicating the accurate distribution and population dynamics of individual species is necessary for conservation and only possible under the correct delimitation of taxa (Agapow et al., 2004).

Sengis are habitat specialists, found over a wide variety of extreme African landscapes from dense forests to barren deserts (Rathbun, 2009) and sengi conservation programs have the potential to promote the protection of a variety of African ecosystems. For example, regions in South Africa may be good candidates for sengi conservation as they support a particular diversity of sengis: 2 species being endemic and seven other species are present, from three genera, (Smit et al., 2008). Since the conservation of the sengis in South Africa would need to include the preservation of their habitat, they could be part of an umbrella species scheme to aid the conservation of other rare and endemic species in their ecosystem (Branton, M. and Richardson, J.S., 2011; Hanser and Knick, 2011). However, widely distributed savanna species like those found in South Africa, seem to adapt readily to cultivation, forestry plantations and human development and probably do not require specific conservation programs, unlike forest dwelling sengis, such as Rhynchocyon udzungwesis (Nicoll and Rathbun, 1990). This emphasises the importance of accurate species delineation for the success of conservation action plans.

 

sengis

 

Conclusions

No species concept is without uncertainty and the importance of organism classification based on adequate sample sizes and combined genetic, morphological and behavioural information cannot be underestimated (Mace, 2004; Zachos, 2013). The variety of species concepts and related cladistics techniques used, can yield variable species numbers and relationships (Agapow et al., 2004; Wheeler and Meier, 2000). Such ambiguity surrounding the composition and relationships within and between populations and communities can make communicating the need for conservation prioritisation arduous (Mace, 2004), potentially leading to a spread of resources that overlook species of great importance to future ecology and evolution than might currently be realised (Frankham et al., 2012).

Even though the increased use of phylogenetics to confirm taxonomy, analyse diversity and inform management, is generally views as a positive development for conservation (Volkman et al., 2014), a case study by Bennett et al. (2014) showed that placing too much emphasis on evolutionary distinctiveness of species during conservation prioritisation elevated costs and increased risk of project failure, resulting in both lower species number and lower total phylogenetic diversity conserved. It is suggested that varying the emphasis on evolutionary distinctiveness in the prioritisation process can result in the opposite effect, an idea also suggested by Tucker et al., 2012.

Despite uncertainties and controversy surrounding species concepts, phylogeny and conservation, without an attempt at systematically acknowledging the unique traits that sets one group of organisms apart from another in ecosystems, there is the potential for the essential ecosystem functions associated with their exclusive ecologies to be overlooked all together (Ceballose and Ehrlich, 2009; Mooney, 2010).

 

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A cooperative function of Allogrooming in a primitive drywood termite species.

Ethology, Project
Adapted from the Dissertation for BSc Zoology, a novel research project, produced only with the observational aid and expertise of Dr. David Crosse, Dr. Nicole Goodey, Prof. Michael Cant, Daniel Blumgart, and Ignatius W. van Rooyen. 

Abstract

 Social group cohesion might occur when individual organisms can gain genetic fitness only by supporting group survival and productivity. While commonly observed, the function of allogrooming in social insects is not well understood. It has been suggested to benefit nestmate recognition, essential to group cohesion. Haplodiploid Hymenoptera have been favoured in cooperation and nestmate recognition studies but using diploid eusocial organisms can bring further insight into cooperation behaviour, as mechanism of social evolution in these species may differ from those in Hymenoptera. Here we aim to  examine the role of allogrooming in maintaining group cohesion. By observing isolated individuals from colonies of the termite Pterotermes occidentis, upon their return to the colony, we found a significant yet temporary increase in allogrooming in response to isolation. We hypothesise that allogrooming might facilitate nestmate Cuticular Hydrocarbon exchange and thus may play an important role in social cohesion, a vital component of cooperation in social animals.

DSCN1429

Introduction

The distribution of resources and competitors in an ecosystem determines animal behaviour in a community, and survival may depend heavily on the use of limited resources that need to be defended from rivals. Social insects often form colonies made up of related individuals that work together to use limited resources for the maintenance and growth of their colony, and when there is more than one colony in close proximity, inter-colony competition for the same limited resources can exist.

Being able to choose between cooperative or antagonistic behaviour when meeting with a conspecific is important for the group cohesion of social insects, and so a means of nestmate recognition is required. The recognition of, not only nest-mates but also instar and reproductive status within a colony, is also crucial for the structure, efficient function and security of an individual member as well as the whole colony: it prevents intra- and inter-specific  parasitism, and the theft of valuable colony resources.

Social insects are thought to use chemical recognition cues to distinguish between nestmates, and non-nestmates competing for the same resources. Cuticular Hydrocarbons (CHCs), found on the exoskeleton of insects, have been suggested to play a particularly important role in chemical recognition cues. Thus, changes in relative CHC abundance between individuals may affect the behaviour towards each other.

Previous studies have shown wide variation in CHC profiles between insect individuals from different colonies and that social grooming (allogrooming) within the social colony of many different species is frequent. It is thought that on of the reasons allogrooming may be necessary is to maintain a common colony profile via the constant exchange of naturally individual and variable CHC profiles.

For this study we used a species of Arizonan drywood termite, Pterotermes occidentis, the workers of which constantly groom each other under natural conditions. We hypothesised that isolation of an individual would lead to an individual’s relative CHC profile differing from that of its colony upon reunion. We predicted that after an isolated termite is reunited with its colony, members would detect the difference in CHC profile, leading to the individual experiencing a higher than average frequency of grooming for a short time before grooming returns to average levels. Aggressive behaviour was not predicted in this species as aggression was very seldom observed during preliminary study.

 

Aims

To examine the role of allogrooming for the maintenance of group cohesion in a species of novel drywood termite, Pterotermes occidentis (Dictyoptera: Kalotermidiae) by testing, via experimental manipulation, whether isolation has an effect on the overall rate of allogrooming observed between isolated individuals and their colony, upon return.

 

Hypotheses 

a. Allogrooming rate will rise from a baseline rate when an individual is reintroduced into its colony after a short isolation period, compared to a non-isolated individual which will maintain a constant allogrooming rate throughout the observation period.

b. There will be a larger increase in Experienced allogrooming than Expressed allogrooming for isolated termites.

c. Allogrooming rate will return to the baseline rate, after a time period of reintroduction of an individual to the colony.

We proposed that such changes in grooming frequency within colonies may be due to natural individual changes in cuticular hydrocarbon profiles of all colony members, leading to a need for continuous CHC transfer to maintain a homogenous intra-colonial chemical profile (Boulay et al. 2000; Nielsen et al., 1999).​

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Literature Review

Cooperation and Altruism

In nature there is an expected tendency for selection to take place on self-interested behaviour and so when it is found that a species has evolved cooperative and altruistic behaviour despite the individuals costs involved, as is the case with many species across animal taxa, Evolutionary Biologists take a close interest.

 A basic situation where supporting group survival and productivity is the only way for an individual to gain genetic fitness encourages the occurrence of social group cohesion (West, 2006). Such situations have been widely studied (Garcia and DeMonte, 2013; Abbot et al., 2011; Korb, 2009; van Veelen, 2009; Dugatkin, 1997).

They are thought to develop when the success of one animal is bound to that of another within a group (often due to matched altruistic behaviour between individuals that share genetic kinship) which increases inclusive fitness and group success while individual direct fitness is reduced. It is suggested that direct fitness interests can be overcome and cooperation achieved if matched behaviour leads to higher indirect and group fitness than can be achieved through selfish behaviour (Frank, 2009).

Altruism has been shown to exist in many different animal social groups (Biedermann and Taborsky, 2011; Duffy, 2002; Faulkes and Bennett, 2001) For example, the study of microorganism social evolution by Kreft (2004) showed that the economical use of common resources increased bacteria group fitness but could only do so at the cost of a decrease in individual growth rate and thus direct individual fitness.

In more complex organisms, recognition based interactions take place between group members and suppression of internal competition within a group influences the occurrence of social group cohesion (Frank, 2009; Tekleab et al., 2009). A study by Bennett et al. (1996) on Cryptomys camarensis, the eusocial Damaraland mole-rat, in which reproduction in a colony is restricted to a breeding pair, showed that not only is there a strong natural aversion to inbreeding, but also repression of ovulation in non-reproductive females by the presence of a reproductive female.

Repression of competition or conflict management behaviour by dominant individuals is essential for group cohesion (Flack et al., 2005). Conflict management often comes in the form of social grooming (allogrooming) of relatives. Madden and Clutton-Brock (2009) demonstrated that in meerkat (Suricata suricatta) societies in which the survival of pups depend on effective group hierarchy management, the frequency of a secondary conflict management strategy is increased when the primary strategy of stress mediation, allogrooming in response to non-resource-focused antagonism by dominant individuals, is reduced. Replacing one strategy with another has a balancing effect, preventing social disruption.

intro termites

 

Allogrooming and Recognition Cues

Allogrooming is a grooming behaviour that takes place between two individuals from the same social group, having both a receiving and providing component exchanged between individuals.

The roles of social grooming are researched in primates at length (Grueter et al., 2013; Lehmann et al., 2006) with less extensive study existing for other mammals such as meerkats (Kutsukake & Clutton-Brock, 2010), badgers (Hewitt et al., 2009), impala (Connor, 1995), cows (Val-Laillet et al., 2009; Sato et al., 1993) and other species such as birds (Lewis et al., 2007; Radford and Du Plessis, 2006).

Even though it is one of the most commonly observed interactions in social insect colonies, the functions of insect allogrooming remain less well understood. Lenoir et al. (2001a) and others (Crozier et al., 2010;Blomquist and Howard, 2003; Boulay et al. 2000) suggest that allogrooming may benefit nestmate recognition.It is known that insect recognition is chemically based (van Wilgenbug et al., 2012; Smith and Bree, 1995) and variable over time (Lahav et al., 2001a) with cuticular hydrocarbons (CHCs) playing a particulary central role (Chaline et al., 2005; Akino et al., 2005; Ruther et al., 2002). Allogrooming is thus proposed by Lenoir et al. (2001a) as not only serving an important hygienic purpose in insect colonies (Fefferman et al., 2007), but also as a mechanism for maintaining a homogenous yet distinct colony odour by facilitating the exchange of CHCs between individuals in a colony.

However, nestmate recognition mechanisms and their functions in group cooperation require further investigation as conflicting theories exist. Kirchner and Minkley (2002) argue that nestmate recognition is mediated through chemicals released by gut symbionts, while alternate explanations emphasising the effects of complex interactions between behavioural and environmental stimuli with genes (Bos et al., 2011; Adams, 1991; Blaustein, 1983).

Being highly eusocial insects, Hymenoptera have been particularly favoured in the study of kin selection driven cooperation, altruism and nestmate recognition. Due to their haplodiploidy, female hymenopteran workers share 75% relatedness with full sisters compared to the 50% relatedness shared by diploid siblings, and thus many Hymenoptera social groups present unusually high genetic kinship.

​Using cooperative Hymenopteran society models, it has been shown that, unlike groups of the most simplistic unicellular organisms (Kreft, 2004; Velicer and Yu, 2003) recognition-based interaction exists between individuals of complex societies, allowing potentially altruistic acts to be directed at specific recipients (Wlodarczyk 2012; van Zwede and d’Ettorre, 2010; Fletcher, 2008). As a result, individually costly behaviour patterns, such as those that transfer recognition cues between individuals are expected to increase overall group productivity and enhance inclusive fitness levels.

 

The Lower Termite, Pterotermes occidentis

Hymenoptera have been favoured in the study of kin selection, cooperation, altruism and nestmate recognition. They are often highly eusocial insects and due to their haplodiploidy, female hymenopteran workers are haploid and share 75% relatedness with full sisters compared to the 50% relatedness shared by diploid siblings. Thus, Hymenoptera social groups tend to present unusually high genetic kinship.​

However, the use of homoploid social organisms in attempts to demonstrate a general underlying mechanism of cooperation is important, offering more insight into the evolution of cooperation. If the evolution of cooperative behaviour and social structure depends on group genetic relatedness (Gadagkar et al., 1991), principles that are true for haplodiploid hymenoptera may not necessarily apply to homoploid eusocial species ​such as the African and Damaraland mole-rats (Burland et al., 2002; Lovegrove, 1991) or termites (Korb, 2008; Thorne, 1997; Bartz, 1979) that all produce only diploid offspring. Like in Hymenoptera species, eusociality is exhibited in termites despite their diploidy, with high levels of cooperation, brood care, a worker caste and repressed reproduction (Thorne, 1997).

Pollock (1996) argues that cooperation under kin selection theory in Hymenoptera can be reduced in the presence of high social competition associated conflict leading to kin avoidance and preferred interaction with non-relatives, when a stable matched behaviour strategy exists between non-relatives. Lower termites are then especially suitable as alternative model subject species of broad concepts like recognition aids for cooperative group organisation since they lack substantial intra-colonial aggression (Olugbemi, 2012; Korb, 2005) which may otherwise be a cause of potentially confounding effects in experimental studies of nest-mate behaviour.

Termite individuals on wood

This project focused on the wingless, immature individuals of the colony: pseudergates (some times referred to as the ‘worker caste’).

 

 

 

Read more about P. occidentis phylogeny, natural habitat, physiology, colony structure, behaviour and the study system used for this project… 

 

 

Selection and Marking Methods

Only the immature worker caste (pseudergates) was used. From each colony 16 individuals were randomly selected, weighed and uniquely marked using different colour combinations of enamel point dots on the head, thorax and abdomen.

​Mark retention was limited and variable due peeling quality of the paint and higher grooming rates experienced by all marked individuals. An optimum period of 2 days existed between marking and first observation: allowing paint to dry and termite recovery after a large amount of handling, yet not losing the mark before the final observation. Marking each individual with multiple dots also reduced the need to re-mark.

At marking, termite restraint was essential in preventing the smearing of paint across important delicate body parts, potentially adversely affecting behaviour and mortality. However, P. occidentis are soft bodied and difficult to handle with forceps for long periods of time, and each focal individual was exposed to a controlled amount of CO2 (10-20%) gas, previously shown as suitable insect anesthetic (Nilson et al., 2006) for 30 seconds, allowing for the application of small paint dots on the head, thorax and abdomen using the round head of a needle dipped in the enamel paint.

8 pairs were formed from the 16 individuals selected per colony by matching termites as closely as possible by weight, and each individual was allocated either to the Test or Control treatment group. Individuals from the Test treatment would be isolated and reintegrated with the colony, whereas those from the Control treatment would undergo no isolation but would otherwise experience exactly the same procedure as Test individuals in every other respect in order to account for effects such as handling stress, and marking on termite behaviour as well as creating a point of reference to which Test termite behaviour could be compared.

This having been done for each colony, a total of 32 pairs of focal individuals resulted. The unique marking, weight, colony number, pair number and treatment group allocation of each individual was recorded for future reference, and all focal individuals returned to their colonies after selection and marking.

Termite marking colours visibility under natural and red light.

Demonstration of the colours used for marking under natural light (used to identify termites outside of observation conditions) and red light under which termite behaviour was observed (used to identify focal individuals under observation).

 

Two marked focal individuals among unmarked nest-mates.

Two marked focal individuals among unmarked nest-mates.

 

Read more about P. occidentis colony structure, how colonies were obtained, handled and incubated in the lab, and termite behaviour in the wild…

 

 

Data Collection Methods

Allogrooming Measure

Due to its frequency and distinction from other behaviours, allogrooming in this species was easily observable and accurately timed. Observations were done in a demountable observation room kept at 26±5°C, under red light with minimum sound and movement vibrations. These conditions were controlled to resemble the natural climate in which P. occidentis is normally found.

Observation intervals lasted 45 minutes, for each individual the trial period was 7 days long and observations took place on Day 0, Day 4 and Day 7, which involved the collection of pre-isolation, post-isolation and post-reintegration grooming rates respectively for Test individuals. Observations for Control individuals took place at the same times.

Test and Control individuals from the same pair were always observed on the same day, though observation times of day were not matched.

Control individuals were returned to their colony after every observation whereas Test individuals were isolated after observation on Day 0, and only returned to the colony on Day 4 and Day 7.Isolation was achieved by placing the individual inside a clear container (5mm x 3mm x 3mm) with a previously unused piece of wood and covered with gauze to allow ventilation but prevent escape. The isolation containers were maintained in the same incubator as the main colonies.

Due to the relatively large area of wood within main colonies and large total number of termites in all but one of the four colonies used, accurate observation of particular individuals within a main colony was impossible under time constraint and observer limitations. As a result observation arenas were made from transparent Perspex (110mm x 110mm x 50mm) and random colony samples were used instead. Each arena held a single 8mm thick slice of wood, particular to the observed colony, elevated on a transparent stand at approximately a 45° angle to a mirrored surface. This reduced the chances for focal individuals to be out of sight, yet allowed termites to move freely.

Before an observation session, a random colony sample of 50 individuals from the three larger colonies would be placed in their observation arena and positioned in the preheated observation demountable to acclimatise for 45 minutes before observations began. The smallest colony contained less than 50 individuals in total and was used in its entirety.

While allowing the colony sample to acclimatise, the focal individuals were identified and placed in a gridded tray, labelled with the identification numbers and mark-colour sequences. These were allowed a 30 minute recovery time in the observation room after handling.

 When the first focal individual was placed in an observation arena with the colony sample, a stop-watch was started and during the next 45 minutes, the start and end times of any allogrooming event was recorded, along with whether it was expressed or experienced with respect to the focal individual. Allogrooming consists of two components that interact with each other, the performer and the recipient, at the same time. Since grooming can also be expressed and experienced at the same time by a single individual, it was important to make a distinction between these two types of allogrooming in recorded data.

At times when multiple grooming events were taking place at once, the start and end time of each was recorded, even if they overlapped. In the event that a focal individual was out of sight, the duration was recorded and later deducted from the total observation time during data analysis.

 Once the observation of a given individual was complete, the individual was not removed from the arena as this would cause disturbance to the entire colony sample. Instead a sample increase was noted and the next observation was continued. When the observations for a particular colony sample was complete, Test and Control focal individuals were either returned to the colony (on Days 0 and 7) or Test termites were placed in separate prepared isolation pots while Control individuals were returned to the colony (on Day 4).

Termitarium set-up

Colonies are kept in incubators. Termitaria (custom designed by Wilmie van Rooyen and produced by Ignatius van Rooyen) are used to house colonies, preventing termite injury and death from being trapped under wooden slices when termitaria are handled. These termitaria also allow quick access to termites and visibility from all sides, while preventing termite escape.

 

Observation arena set-up.

Left: Observation area (custom designed by Wilmie van Rooyen and produced by Ignatius van Rooyen) with wood elevated on serrated edges so that termites could move freely without being trapped between wood and perspex. The arena was placed over a mirror so that all sides of the wood could be observed at once. Right: Observation took place under red light in a temperature an noise controlled room.

 

 

Solid Phase Microextraction

In addition to behavioural observation, Solid-Phase Microextraction (SPME) was used to collect cuticular hydrocarbon samples from focal termites to be used in a separate but parallel future investigation of changes in individual cuticular hydrocarbon profiles in response to isolation (Singer, 1998). For this, all focal termites were swabbed with a thin polymer-coated fused fiber which collected cuticular hydrocarbon samples from the individuals.being alive nor dead could be ruled out).​

The results of this study are not presented or discussed here, however attaining the cuticular hydrocarbon sample required that focal individuals were mechanically restrained for a short amount of time before each observation, the handling stress of which possibly affected the general behaviour that was then observed and the possible effects on the results of this study will be discussed.​

 

Mortality Survey

After all observations were complete for each treatment group, a post-experimental mortality survey was conducted to investigate the effect of treatment group on focal termite mortality. We collected all focal individuals 70 days after the first isolation took place and for each individual recorded whether it was found dead, alive or remained unfound (so neither the possibility of being alive nor dead could be ruled out).​

Data Analysis Methods

Allogrooming Analysis

Out of the 32 termites pairs which were selected and marked for observations, 25 pairs of complete allogrooming data sets were obtained due to the death of one or both individuals in 7 of the pairs during the course of the experiment. All statistical tests were performed using the statistical analysis software package, R.

 A series of 11 different statistical tests on the same two sets of data were performed at a 95% confidence level. This meant that there was a 43% chance of Type 1 error (1 – 0.9511) occurring.

 Using the Start and End times of each allogrooming bout, the duration of allogrooming bouts were calculated (End Time – Start Time=Grooming Duration). Grooming Durations for each individual on each observation day were then used to calculate the proportion of time the focal termite experienced grooming (Sum of Experienced Grooming Durations/Total Observation

 Duration=Proportion) and the proportion of time the focal termite expressed grooming (Sum of Expressed Grooming Duration/Total Observation Duration=Proportion). The proportion of time spend allogrooming was representative of the allogrooming rate. First the collected data was illustrated in line-graph form, comparing the mean proportion of time spent experiencing and expressing grooming on each observation day (0, 4, and 7) for Test and Control​​ treatment groups. It was determined that Expressed Grooming data was not normally distributed while Experienced Grooming data was normal.  This was showed in the form of histograms and doing an analysis of variance on all the data using the Shapiro-Wilk normality test.

​Independent paired difference tests were then used to determine whether there is a significant difference in means between Test and Control treatments, on Day 0, 4 and 7, for Experienced Grooming time proportions (Paired t-tests) and Expressed time proportions (Wilcoxon Signed rank tests).

By plotting means against variances for each observation day, it was found that the variance increased with mean. Consequently, Kruskal-Wallis rank sum tests were used to demonstrate whether there is significant difference in means of observation days within Test and Control treatments, for Experienced Grooming proportions and Expressed Grooming proportions. Some differences were shown to exist and consequently, paired difference tests (Paired t-tests for Experienced Grooming data and Wilcoxon Signed rank tests for Expressed Grooming data), were used to determine where these differences in means lay and what their magnitudes are: for each treatment group we did the appropriate paired difference tests with Day 0 versus Day 4, Day 4 versus Day 7, and Day 0 versus Day 7.

Mortality Survey Analysis

Post-experimental mortality data was analysed using the Chi-squared test to determine whether treatment group had an effect on mortality.

 

 

Results

Allogrooming

The data for the proportion of observation time that focal individuals were groomed by colony members (Experienced Grooming) and groomed colony members (Expressed Grooming) show that Test and Control individuals spent a greater proportion of time being groomed than grooming overall (Fig.1)

Referring to Table 1, the difference for mean Experienced Grooming proportions between Test and Control treatments was found not to be significant on Day 0 (P=0.32), nor on Day 7 (P=0.86), but was significant on Day 4 (P=0.04). For the mean Experessed Grooming proportions, once again no significant difference was determined between Test and Control treatments on Day 0 (P=0.67) or Day 7 (P=0.48) but on Day 4 the difference was again significant (P=0.031) as shown in Table 1.

A significant difference existed between observation days within both Test and Control treatment groups (P=0.0022 and P=0.046 respectively) for Experienced Grooming proportions (Table 2).

For the Test group, mean Experienced Grooming proportions were not significantly different between Day 0 and Day 7, but significant differences lay between Day 4 and Day 0, and between Day 4 and Day 7. The same pattern was found for the Control treatment group but at a lower significance (Table 2).

For Expressed Grooming proportions, a significant difference was found between days within the Test group (P=0.0025) but not within the Control group (P=0.093), as shown in Table 2. For the Test group, it was indicated that that there was a significant difference between Day 0 and Day 4 and between Day 4 and Day 7, but not between Day 0 and Day 7 (Table 2.).

Although, no significant difference in grooming proportions between observation days was found for the Control group using the Kruskal-Wallis rank sum test, Fig. 1 does illustrate some elevation in mean Expressed Grooming on Day 4. This was investigated and no significance existed in the differences between Day 0 and Day 4, nor between Day 7 and Day 0, but between Day 4 and Day 7, the difference was of some significance (P=0.024) as shown in Table 2.

To sum up all the data, the above described relationships are illustrated in Fig. 1. Larger peaks in mean Experienced Grooming and mean Expressed Grooming time proportions on Day 4, as well as higher levels of significance in the differences between Day 0 and Day 4 (Table 2), are shown for the Test treatment group than for the Control treatment group; and on Day 7 declines in mean grooming proportions resembled those found on Day 0.

 

Untitled

 

Comparing treatment groups

 

Comparing Days

Mortality

Finally, Fig. 2 illustrating post-experimental termite mortality data from all 64 initially marked focal individuals indicates that there may be a relationship between the treatment group which individuals belonged to and their mortality.

It might be concluded from the bar graph that more Test individuals were found dead, and fewer were found alive compared to Control individuals. Also, that more Control individuals remained unfound and so potentially alive, which wasn’t the case for Test individuals. Equal amounts of Test and Control individuals were found indistinguishable from other marked individuals within the colony.

 

mortality

 

Discussion

In this experiment we tested whether there would be a change in allogrooming rate experienced and expressed by individuals of P. occidentis individuals upon reintroduction to the colony after a period of isolation. Our aim was to assess the role of allogrooming in the maintenance of group cohesion for a lower termite species. We found a significant increase in mean allogrooming rate in response to isolation from the colony for both components of allogrooming.

As we predicted, our results show no significant difference on Day 0 and a significant allogrooming increase after 4 days of isolation. We also observed no aggressive reactions from the colony towards returning individuals. This is feasibly indicative of a change in the isolated individual, detected by its colony upon return, triggering a behavioural response.

We suggest that during isolation, no opportunity existed for the homogenisation of CHC profiles between the colony and the isolated individual. A slight change in the individual’s profile distinct from that of the colony may have occurred as have been shown possible in various ant species (Nielsen et al., 1999; Liu et al. 2001; Vander Meer et al., 1989), and could have been detected by the colony. Longer, more frequent grooming bouts between the focal individual and colony members could be an attempt to re-homogenise the colony’s chemical profile.

These results support the findings of Lenoir et al. (2001a) and Boulary et al. (2004), showing that colony members of two ant species, Aphaenogaster senilis and Camponotus fellah, react sociably towards returning individuals after a period of short isolation (approximately 3-10 days) and that increased social behaviour was likely to promote the re-homogenisation of colony odour.

However, both studies noted aggressive behaviour of colony members towards returning nestmates after a longer period of isolation (approximately 10-40 days). Aggression has been shown as part of kin recognition systems (Ichinose and Lenoir, 2009;Suarez et al., 2002) and a lack thereof in some social insect species, including P. occidentis, can be puzzling since strong intraspecific resource competition often exists in eusocial insects due to valuable food sources (Shellman-Reeve, 1997). Effective kin recognition could allow distinction between nestmates and non-nestmates (Sobotnik et al., 2008; Lenoir et al 2001b) and assessment of the most appropriate interaction to display such as social rejection (Kaib et al., 2002) or acceptance (Holway et al., 1998)

We used a short isolation period and valuable future study lies in lengthening and varying this isolation period, to explore the reactions towards nestmates in P. occidentis after a longer time away from the colony. These results can then be analysed in the light of genetic relatedness. For example, Kidokoro-Kobayashi et al. (2012), suggests that unicoloniality might explain the lack of aggression seen in some social insect species, while Fuller et al (2004) showed that, since both genetic and environmental factors change with geographic location, aggression towards non-nestmates increases with geographic distance from a nest. It is explained that colonies closer to each other are more likely to share genetic similarities due to colony separations earlier in time. This makes the location of a colony’s origin also an important aspect of future study, as this was not included as a factor in our work.

Allogrooming has hygienic purposes (Fefferman et al., 2007) the effect of which was also not considered during our experiments and holds potential for future investigation discussed further on. In dampwood termite colonies which have high pathogen loads, allogrooming has an important role in the removal of pathogens and parasites (Rosengaus et al., 1998), and has been reported infrequent in species of drywood colonies which have naturally very low pathogen loads (Rosengaus et al., 2003). However, allogrooming is still frequently observed in P. occidentis colonies possibly supporting the hypothesis that it is needed to facilitates the exchange of CHCs between individuals of eusocial insect colonies (Crozier et al., 2010; Lenoir et al., 2001a; Boulay et al. 2000) and thus, its role in group cohesion, possibly via kin recognition, can be essential for cooperation in social animals (Garcia and De Monte, 2013).

In addition, we show fluctuation in allogrooming rate for the non-isolated control individuals, which was unexpected. On Day 4 the increase in grooming rate of non-isolated individuals was significant for both components of allogrooming. These were of lower significance than the increase seen for isolated individuals, and the difference between the increased rates of isolated and non-isolated groups on Day 4 was significant.

A possible explanation may be that during a given observation, a non-isolated individual may have been inadvertently affected by a possible continuous response of the colony sample to the presence of an isolated individual during a prior observation. Lenoir et al. (1999) discussed a chemical integration period which exists in newer members of ant colonies and we postulate a similar occurrence in termites.

A way in which such an effect could be minimised is by renewing the colony sample before each observation, allowing time between observations for the colony to recover from the response to the isolated individual.

For both isolated and non-isolated groups, the increase in mean experienced allogrooming rate was more significant than the mean increase in expressed allogrooming rate. However, the variance of allogrooming rate across Day 0, 4 and 7, within the isolated group was more significant than within the control group.

This was predicted as we expected the colony members to focus on isolated individuals when returned. Since we recorded all observations in respect to individuals, and each termite can only groom one other individual while being groomed by many, a higher increase for experienced allogrooming can be recorded. As stated above, fluctuation in grooming rate for non-isolated individuals we found was not predicted but this concept may apply to the similar pattern in allogrooming found for the non-isolated group.

After a period of isolated termite reintegration with their colonies, the allogrooming rates of all individuals had lowered significantly by Day 7, and closely resembled the basal rate recorded on Day 0.The difference between rates recorded before isolation on Day 0 and after the reintegration period on Day 7 was not significant for either component of allogrooming, in either treatment group.

As already mentioned, we explain these results by proposing a mechanism involving CHCs. For example, if the presence of an anomalous CHC profile might trigger increased allogrooming, homogeneity may be achieved in the colony-specific CHC profile again, after some time. This could then mean that the cue for increased allogrooming also dissipated and allogrooming returns to a normal rate as a result (Singer, 1998; Vander Meer et al., 1989).

We discovered that both isolated and non-isolated individuals experienced overall more allogrooming than they expressed, even at the basal rate collected on Day 0. This finding was surprising because if our sample of focal individuals accurately represented the colony populations they were sampled from, it would not be rational for every termite to received more grooming on average, than it performs.

A possible reason for a lack in expressed allogrooming could be due to handling stress experienced during Solid-Phase Microextraction hydrocarbon sampling since this was a physically disruptive process for this soft-bodied species.

Though quantifiable data was not collected, there seemed to be variation in the stress experienced through SPME sampling as it is not a precise process, whereas this variation was not obviously reflected in the difference in overall expressed and experienced allogrooming.

On the other hand, all focal individuals were marked and during observation, un-marked (non-focal) colony members were noted as particularly attentive to the paint markings when grooming. This causes us to put forth a more plausible explanation, similar to one mentioned earlier: all focal individuals received more frequent grooming than they were able to perform at a given time, even before isolations took place, and we speculate that this may be a result of the hygienic function served by allogrooming.

In light of the fact that some drywood termite species exhibit very low levels of allogrooming, and their colonies are relatively pathogen free, potential fascinating questions are raised such as the reasons some drywood termites retain allogrooming while others do not and the practical degree to which group cohesion is affected by allogrooming. These hold the potential for manipulation experiments using markings on individuals within a colony and testing a response.

However, since there is also little research on the effects of enamel paint (or other marking mediums) and CO2 as an anaesthetic on termites, it may well be that these also had an effect on their behaviour. In the past, CO2 been shown effective and safe for invertebrate use (Cooper, 2011), possibly even blocking the effects of handling stress (Pankiw and Page, 2003) however some studies point out possible disadvantages Dombrowski et al. 2013; Colinet and Renault, 2012).

A study by Miramontes and DeSouza (1996) has demonstrated increased mortality rate due to social isolation the termite, Nasutitermes cf. aquiline. The results of our mortality survey do not support this for short isolations of this species as it showed no significant relationship between treatment and the mortality which occurred up to 40 days after the final observation. However, a number of focal individuals had lost their marks by the time the mortality survey was taken and so were indistinguishable from other termites and surveying at shorter time intervals would present more useful results.

Colony polymorphism, caste of focal individual and colony size may all affect social behaviour (Nandi et al., 2013; Aviles et al., 2004; Crosland et al., 1997; Oster and Wilson, 1978) but were not controlled for in this study. Since focal individuals and colony samples were randomly selected from each colony, and the colony sizes ranged from 30-170 individuals, the representation of each colony’s behaviour patter n was reasonable. Future more advanced statistical analyses may be done using methods which account for mixed effects such as caste and colony size.

The importance of group cohesion in survival and productivity of cooperative insect groups has been thoroughly described (Hamilton et al., 2009) and a recent study by Lihoreau and Rivault (2009) showed the value of kin recognition to the cohesion of a social life in the cockroach, Blattella germanica. The kin recognition properties of CHCs have been shown to exist even in sub-social species such as Stegodyphus lineatus, a sub-social spider (Grinsted et al., 2011).

Other than pathogen and parasite control, allogrooming may serve an adaptive role as a mechanism of group-specific CHC exchange between individuals within a colony, which would enable nestmate discrimination and protection of resources. There is also evidence that the CHCs are influenced not only by the environment (Wagner et al., 2001; Silverman and Liang, 2001) but also genetics (van Zweden et al., 2010; Dronnet et al., 2006; Page et al., 1991). If kin selection plays a role in whether or not one individual displays allogrooming behaviour, and as a result influences the cohesion of a group according to a genetic relationship, there may be inclusive fitness benefits for allogrooming.

Finally, having obtained good indication that allogrooming can fluctuate in accordance with whether or not an individual has had recent contact with its nestmates, and given that allogrooming can be widely recognised in many social species, we allogrooming as having a potentially recognition based function, essential for the effective cohesion of a social group. Through the continued interest in group behaviour and the study of its common underlying principles, we can come to gain better understanding around the evolution of cooperation under the laws of natural selection.

 

 

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Pterotermes occidentis: colony structure, eusociality and research project study system.

Ecology, Ethology, Natural History, Project
Part of  a novel research project serving as BSc Zoology dissertation, produced only with the observational aid and expertise of Dr. David Crosse, Dr. Nicole Goodey, Prof. Michael Cant, Daniel Blumgart, and Ignatius W. van Rooyen. 

 

P. occidentis Phylogeny

P. occidentis is a primitive (lower) termite species (Oder: Dictyoptera; Family: Kalotermitidae). Termites share a common ancestor from the cockroach family (Cryptocercidae) and can be thought of as a specialised form of cockroach (Eggleton 2011). After decades of unclear hypotheses and poor taxon sampling, 7 majour termite clades (Families) have been decided upon as illustrated in the diagram on the right.

Phylogeny termites

 

P. occidentis Natural Habitat

The ecological niche that P. occidentis fills in the North American Sonoran Desert to which they are endemic, is that of decomposers. They can commonly be found nesting in dead Arizonon Cercidium trees.

What little water they obtain comes from moisture found in their food source, rare rain storms and dew fall. They depend on the protection from extreme desert weather conditions that their nest, usually enclosed in a dead tree stem and branches, provides.

In September 2011, Prof. Michael Cant and Nicole Goodey extracted P. occidentis colonies from their natural habitat, near Tucson, Arizona for use in research. The colonies were re-established under controlled lab conditions at the Center for Ecology and Conservation, Cornwall.

I was introduced to this highly cooperative primitive termite species in January 2012, when I started working as a lab intern. Joined later by Dr. David Crosse, we began to refine laboratory techniques, starting work on angles of study based on previous work involving primitive eusocial insect species, and theories of cooperative animal behaviour and evolution.

 

 

 

P. occidentis Physiology

P. occidentis is soft-bodied. Workers lack pigmentation while Reproductives and Soldiers are usually an auburn brown colour. These are hemimetabolistic insects meaning they undergo stages of development (metamorphosis) without a pupal stage, but molting  between developmental stages to grow to maturity.

 

 

 

Cuticular Hydrocarbons (CHCs) found on the cuticle of insects are often cited as being particularly important for recognition cues in social insects however this is still a controversial theory.

Correlation studies have shown a wide variation in the CHC profiles between individuals from different colonies, and over time.  These variations in CHC’s between individuals may affect costly social behaviour of insects in a way which can be recorded and used to shed light on the mechanisms of social evolution.

 

 

P. occidentis Colony Structure 

P. occidentis colony life is a complex social system. The colony consists of different termites each of which specialises in a different role.

Pseudergates (sometimes called ‘workers’) lack pigmentation, are soft bodied and have no weaponry, although some may have wing buds at certain stages. Pseudergates grow in size, molting into different stages. They are mainly observed feeding and cleaning the colony, responsible for caring for eggs, the reproductives and soldiers, as well as building the nest.

Pseudergates also care for each other via interactions called trophalaxis and allogrooming. It is thought that they may also molt into soldiers and have been observed in the process of molting into neotenic reproductives in the event of the death of the original reproductuves. Little is known about the mechanisms of determing whether an individual remains a pseudergate, or develops into a solider or reproductive, at a certain point in time. However, it is thought that there may be a connection between environmental conditions, the current number of soldiers or reproductives present, the needs of the colony and whether or not new soldiers or neotenic reproductives are observed to appear.

The majority of the colony is made up of pseudergates at various stages of molt. Some grow wings when food is scarece in preparation for flying away to find a new food source and to start a new colony elsewhere. However, this transformation is reversible and if the food souce is replenished somehow, they lose their wing buds. Little is understood about how these termites determine the size of the food source and the amount of nutrition available at any point in time, or how they know the size of the colony itself.

Soldiers are dark brown in colour,  armoured, have very large heads equiped with pincers and exhibit agressive behaviour more often than other members of the colony. There are relatively few soldiers in the colony and they are responsible for nest defence.

P. occidentis nests are sometimes at risk of invasion by a rival colony in search of a new source of food, or interested in  merging colonies which involves destroying a colony’s current reporductives. Neither situation would be beneficial for the invaded colony as sharing their rare food source with a rival colony threatens their survival. They may also be genetically unrelated to the invading reproductives which means there would be a break down in the altruistic functions of the colony.

In the event of such colony invasion, soldiers may use their large heads to block the tunnels of the nest and their pincers to attack invaders. In this species, the pincers are nore particularly effective and P. occidentis seem to exhibit much lower levels of aggression than many other termite species.

Reproductives are larger than pseudergats but less bulky than soldiers. The older the reproductive, the darker its brown pigmentation and they also posess harder bodies than psuedergates but that are less armoured than soldiers. Each colony has a king and queen whose sole purpose it is to reproduce. Reproductives are less active than other colony members and are usually found together, surrounded by a dense gathering of pseudergates, constantly grooming and feeding their king and queen.

P. occidentis are hemimetabolistic insects, hatching from eggs as nymphs. They appear to be able to molt through nymphal stages, some eventually ending up as fully reproductive and others soldiers. The majority of individuals in the colony, though molting and growing in size, or even growing wing buds, reach neither the reproductive or soldier stage.

It is very important for the survival and efficient function of the colony that individuals of a colony at different stages can recognise each other as being both different, with different functions within the colony, as well as relatives from the same colony, and therefore entitled to the same colony resources and services.

I have observed that when a P. occidentis individual from one colony is introduced to members of a different colony, it is ignored. In other termite species, aggression between the colony members and the unrelated individual may be observed, but even though a non-aggressive approach to a stranger might seem counter productive for the security of the colony, it may work to prevent the occurrence of free riders from other colonies taking advantage of the social and resource benefits of a colony as previous studies suggest that social interaction is essential for the survival of individuals from primitive termite colonies.

Little is known about the mechanisms through which P. occidentis individuals distinguish between relative and non-relative individuals. Inhabiting tree stumps and branches means that termites live in total darkness most of the time and so do not have well developed eyesight, but rather seem to be able to detect changes in lighting. CHC detection or the use of gut symbionts as ways of sharing common markers and recognising each other have been suggested and researched.

In a very dry environment, where temperature extremes are not uncommon and essential resoures are hard to come by, the colony works together to grow and produce many members that all share 50% of their genes with each other as well as with their kign and queen. During this process, they pay a service to the ecosystem by re-working dead plant matter and in doing so, replenish the environment with essential nutrients for it’s continues existence and development.

 

 

 

P. occidentis Behaviour 

Common characteristics are found in species that have developed sociality and eusociality:

 1. Mating Systems: inbreeding with periodic out-crossing (for reduction of inbreeding costs) leads to high relatedness within a colony.

 2. Parental Care: (at least to some extent) allows for overlapping generations within a related social group.

 3. Helper evolution: due to high adult mortality, long periods of offspring dependence or delayed age of reproduction.

 4. ‘Fortress Defenders’: primitive (lower) termites often live inside their food source.

 5. Other factors: Mutualistic interactions and restricted dispersal can also foster the evolution of sociality.

behaviour termites

 

P. occidentis are ‘fortress defenders’:

Three conditions are needed to explain the occurrence of eusociality in Fortress Defenders:

 – Food and shelter are enclosed in the same resource: the combination of being a long-lasting habitat making and food source makes for highly valuable.
– Due to high value, there is strong competition for the resouce .
– Due to competion, selection should promote evolution of effective defence among rival organisms.
Nestmate Recognition: 
The dry wood that P. occidentis live in and feed off is their most valuable resouce. The evolution of social behaviour is closely linked to the need to defend a valuable resource.
Recognition of nestmates, kinship, caste and reproductive status is crucial for individuals and for the colony as a whole: it is important for knowing who to share limited resources with.
The ability to effectively discriminate works to prevent intra- and interspecific parasitism and theft of limited colony resources.
Allogrooming:

Recognition cues in social insects are thought to be chemical, with hydrocarbons found on the cuticle of insects often cited as being particularly important. According to previous work, CHC composition may change over time and between colonies and individuals.

Because termite colony members may have naturally individual profiles, a constant hydrocarbon transfer may be needed to maintain a similar overall colony profile [Boulay et al. 2000, Campoutus fellah colony integration: worker individuality necessitates frequent hydrocarbon exchanges. Animal Behaviour 59, 1127-113.] and thus grooming between members of the same colony (nest-mates) is frequent.

Allogrooming is found in many social insect species and is a behaviour thought to facilitate the exchange of cuticular hydrocarbons involved in recognition cues.

ants

For many social insects that are haplodiploid (producing some offspring with higher relatedness than others), well known theory of inclusive fitness is accepted to explain social behaviour. However, since termites are homoploid (producing only diploid offspring), inclusive fitness does not always explain termite social behaviour, necessitating further study. 

 

Read the full research study of Pterotermes occidentis completed for the Dissertation in BSc Zoology in 2013… 

 

Read the peer reviewed article published in the Royal Society Open Science online journal in 2016, as a results of the above mentioned work…

 

 

P. occidentis Study System

study system termites

In September 2011, 4 colonies of varying instar composition and size (34, 112, 139 and 170 individuals) were extracted from dead Cercidium microphyllum trees at four different nesting sites near Tucson, Arizona.

​Each colony was contained inside a transparent Perspex box (206mm x 306mm x 31mm). Inside, slices of 8mm thick Cercidium microphyllum wood was packed next to each other to form an observable termitatium for each colony.

​The colonies were maintained in an incubator set at 28±2°C from 09:00 to 17:00 and 18±2°C from 17:00 to 09:00, on a corresponding Light-Dark cycle, and at a constant low humidity. Water was provided in the form of droplets generously sprinkled over the wood every two weeks.

​Each colony was allocated separate equipment and wood stock to control for cross-contamination of colony specific cuticular hydrocarbon compounds.