Browse Subject Areas

Click through the PLOS taxonomy to find articles in your field.

For more information about PLOS Subject Areas, click here.

  • Loading metrics

Forestry Alters Foraging Efficiency and Crop Contents of Aphid-Tending Red Wood Ants, Formica aquilonia

Forestry Alters Foraging Efficiency and Crop Contents of Aphid-Tending Red Wood Ants, Formica aquilonia

  • Therese Johansson, 
  • Heloise Gibb


Forest management alters species behaviours, distributions and interactions. To evaluate forestry effects on ant foraging performance, we compared the quality and quantity of honeydew harvested by ants among clear-cuts, middle-aged and mature spruce-dominated stands in boreal forests in Sweden. Honeydew quality was examined using honeydew collected by squeezing the gasters of laden Formica aquilonia workers. We used fifteen laden individuals at each study site (four replicates of each stand age) and analysed honeydew chemical composition with gas chromatography-mass spectroscopy. To compare the quantity of honeydew collected by individual ants, we collected and weighed five ants moving up and five ants moving down each of ten trees at the twelve sites (totally 1200 ants). The concentration of trehalose in honeydew was lower in clear-cuts compared with middle aged and mature stands, and similar trends were shown for sucrose, raffinose and melezitose, indicating poorer honeydew quality on clear cuts. Concentrations of the amino acid serine were higher on clear-cuts. The same trend occurred for glutamine, suggesting that increased N-uptake by the trees after clear cutting is reflected in the honeydew of aphids. Ants in mature stands had larger heads and carried proportionally more honeydew and may therefore be more efficient foragers. Human alternation of habitats through clear-cutting thus affects food quality and worker condition in F. aquilonia. This is the first study to show that honeydew quality is affected by anthropogenic disturbances, likely contributing to the reduction in size and abundance of F. aquilonia workers and mounds after clear cutting.


Anthropogenic disturbance, mainly through urbanization, forestry and agriculture, has severe impacts on ecosystems worldwide, affecting ecosystem processes, habitat structure and species composition [1], [2], [3], [4], [5]. Effects on species interactions, such as competition, predation and parasitism are also commonly reported [6], [7], [8]. Although effects of anthropogenic disturbances on pollination are well known [9], [10], effects on other mutualisms, such as that commonly occurring between ants and hemiptera, are poorly understood [11].

Mutualisms with hemiptera are vital for ants in most ecosystems [12], [13]. The digestive systems of behaviourally and numerically dominant arboreal ants are highly specialised for the kind of carbohydrate-rich and protein-poor diets obtained from feeding on hemipteran exudates [14], [15]. Energetically expensive levels of activity and aggression may be promoted by the reliable sugar resource provided by the hemipterans [16], [17]. Because ant-hemiptera mutualisms result in significant quantities of energy being available to ants and therefore promote activities such as predation and seed dispersal that have broader effects on ecosystems, ant-hemiptera mutualisms may be considered to be keystone interactions [18].

Plant exudates play a key role for the carbon and nitrogen budgets of many ant species [19], [20]. Honeydew contains a broad range of sugars and amino acids of varying importance to ants. Previous studies suggest that honeydew quality varies between different environments [21], [22], [23]. Food quality may alter caste determination and size variation within castes [20], [24], with poor quality food resulting in smaller adult body size [25] and potentially altering foraging efficiency and size-dependent allocation of tasks [26]. Differences in food quality resulting from anthropogenic disturbances may therefore have significant effects on the success of ants.

Despite the keystone role of ant-hemiptera mutualisms, few studies have examined how they are affected by anthropogenic disturbances. In Scandinavia, intensive forestry has dramatically changed the structure and species composition of the boreal forest, with significant impacts on many species [27], [28], including the dominant red wood ants of the Formica rufa group [29], [30]. Land management alters ant use of hemipteran resources [11], [25], [31] and clear-cutting results in reduced colony survival, rates of reproduction and immunity for red wood ants [32], [33], [34]. Approximately 85% of the dry mass of the diet of red wood ants consists of honeydew from arboreal aphids [35], [36], yet it is unclear whether forest management affects the quality of this resource or the capacity of individual workers to harvest it. In this study, we address the following questions: 1) Does the composition of sugars and amino acids in ant-collected honeydew depend on stand age? and 2) Does worker body size have consistent effects on honeydew load in stands of different ages?


Study area and species

All study sites were situated in Norway spruce (Picea abies) dominated forest in the middle boreal zone [37] of northern Sweden between the latitudes of 63.6°N and 64.5°N and longitudes of 19.7°E and 20.7°E. Scots pine (Pinus sylvestris) and birches (Betula pendula and B. pubescens) were also common in the stands. The herb layer was dominated by dwarf shrubs (mostly Vaccinium myrtillis) and mosses (Pleurozium schreberi, Hylocomium splendens, Sphangnum spp.). On clear-cuts, Deschampsia flexuosa often dominated the herb layer. Soils were moist and of the sandy moraine type.

Formica aquilonia Yarrow is the most common F. rufa group species in the central boreal region of Fennoscandia [38]. In boreal forest, red wood ants (Formica rufa group) are ecologically dominant and form mutualisms with aphids [31], [35], [39]. In the study sites, F. aquilonia tends the aphids Cinara pruinosa (Hartig) and C. piceicola (Cholodkovsky)(pers. obs. by Heloise Gibb, identified by R. Danielsson, University of Lund). Previous studies report that F. aquilonia is affected by forest succession, being more common in old forests and in larger old-forest fragments [40].

We selected 12 study sites with established populations of the red wood ant Formica aquilonia for the study. Four study sites were in mature stands (tree age 80–100 years , mean basal diameter 7.4 cm, mean height 17.9 m), four in middle aged stands (30–40 years , mean basal diameter 4.9 cm, mean height 8.3 m) and four on clear cuts with 5–10 retention trees per ha (1–4 years, mean basal diameter 1.2 cm, mean height 2.1 m). Basal diameter includes all trees including saplings >1 cm. Stands of different ages were geographically interspersed. Each study plot supported several nests of F. aquilonia. All necessary permits were obtained for the described field studies.

Honeydew collection

Honeydew was collected from fifteen laden F. aquilonia workers travelling down spruce trees after harvesting honeydew at each of the twelve study sites in July 2008. Ant crop contents have been shown to closely resemble the source, although there can be minor changes in sucrose, glucose and fructose concentrations due to enzymatic activity [12]. We assumed that any changes in sugar concentrations as a result of enzymatic activity would be consistent amongst stand ages because ants were of the same species and collected at similar distances from their nests. We did not directly control the source of the honeydew since we did not have access to the tree crowns while collecting honeydew. However, aphid surveys in the same stands were used to determine the main honeydew producers in the stands.

We collected honeydew from the crops of worker ants by gently squeezing their gasters, such that they regurgitated liquid into a 1.5 ml eppendorf vial. Cloudy samples representing contamination with haemolymph were discarded (as per Blüthgen et al. 2004) [21]. We weighed each vial before and after collecting the honeydew to obtain an exact weight for each sample. To prevent degradation, samples were kept on ice in the field, and then stored at −80°C on return to the laboratory.

Chemical analyses

Samples weighing between 1 and 10 mg were analysed, resulting in 10–12 samples per stand and a total of 137 samples used in the analyses. The chemical composition (sugars and amino acids) of the honeydew were analysed with gas chromatography-mass spectroscopy (GC-MS) at the Metabolomics facilities at Umeå University.

We used solvent-based extraction with internal standards added to the sample prior to extraction. The sample and 250–2525 µl of extraction medium so that the ratio sample/extraction medium was kept at 0,002 (chloroform/MeOH/H2O; 2∶6∶2) including stable isotope reference compounds were added to an Eppendorf tube. The extraction was performed in an MM 301 vibration mill (Retsch GmbH & Co. KG, Haan, Germany). After extraction, the samples were derivatized 16 h of at room temperature. For the GC-MS analysis, one µL of the derivatized sample was injected by an Agilent 7683 autosampler into an Agilent 6890 gas chromatograph (J&W Scientific). The column effluent was introduced into the ion source of a Pegasus III time-of-flight mass spectrometer, GC-TOFMS (Leco Corp., St Joseph, MI, USA). All data were processed by ChromaTOF (1.00) software (Leco Corp.). Each sample was normalized before the multivariate analysis. Normalization is essential if the samples are not identical, e.g., if there are differences in sample weight or volume, or a purification or derivatization step is involved that might result in variations in recovery. We divided the response values (area counts) by the sample weight and the intensity of one or more internal standards. For a more detailed description of the extraction, derivatization and analysis steps see Gullberg et al. [41].

Aphid surveys

We performed surveys of aphids from spruce trees with honeydew harvesting ants present, on clear days in July 2006. We used eight sites in each age category. [31]. Aphids were counted and some specimens were identified in the laboratory in 2006. In 2011 we did a more detailed determination of samples from 10 of the stands (4 clear cuts, 3 middle aged stands and 3 old stands) so that the assemblage composition of aphids could be compared among stand types. Three branches were taken from five different spruce trees or saplings in each of the sites. Branches were collected from the upper canopy, just below the tree crown, in all site types as it was not possible to safely reach the crown in old stands. We used ladders to access canopies in middle-aged stands and experienced climbers to reach the canopy of spruce trees in old stands. At all sites, branches were cut at the base and bagged. On the ground, we beat the branches and collected aphids and other insects were from the beating tray using an aspirator. The stands selected for the more detailed analysis were the same stands that were used for the honeydew sampling. However one old stand from the same area but not sampled for honeydew was added to increase the sample size for old stands.

Mass of honeydew harvested

To compare the mass of honeydew collected by individual ants in different stand ages we collected ants moving up and down trees on fine days in July 2008. Ten spruce trees with F. aquilonia activity were selected at each site between 0.5 and 35 m from a central nest. We collected five ants moving up and five ants moving down each of the ten trees at four sites belonging to each of the three stand ages for a total of 1200 ants. We did not specifically select ants with laden and non-laden gasters because we aimed to compare harvesting efficiency per ant. To effectively collect ants we used an aspirator built from a battery driven vacuum cleaner. This method was selected as ants proved less likely to squirt formic acid (and therefore lose weight) when removed using an aspirator than by forceps. Ants were placed in a cold box (approximately 5°C) in the field and were later frozen for 3 days at −20°C to ensure that they were killed. Ants were weighed individually in the lab and any needles or prey items were removed before weighing.

Statistical analyses

To test for differences in honeydew composition among stand ages we used PERMANOVA (permutational multivariate analysis of variance) in Primer 6 [Primer 42,43]. We performed separate analyses for total honeydew composition, carbohydrates and amino acids. Because the concentrations were not directly comparable among compounds, we standardised each compound (so that the sum of area counts for each compound from all samples was 1 (100%)) and fourth root transformed the data before analysis to both reduce the influence of the most abundant compounds and assess changes in proportional abundance of compounds [44]. We used the Bray-Curtis similarity measure which is not affected by joint absences [45], 5000 permutations of the data, and performed the permutations of residuals under a reduced model. Pair-wise tests were used to detect which stand ages differed from each other [43], [46].

We tested for differences among stand ages for identified carbohydrates and amino acids with relevance to ants using the GLM procedure in SAS 9.1 [47]. After examining the residual plots, the data was log(x+1)-transformed before the analysis to correct for heterogeneity in variances. If significant stand age effects occurred, we examined the effect using Tukey's honestly significant difference (HSD) test.

We tested for differences in abundance of the most abundant aphids and their relation (quota Cinara pruinosa/Cinara piceicola) among stand types using Kruskal-Wallis test in JMP 8 [48]. When we found significant differences we performed pair wise comparisons among the stand types using Mann-Whitney U-tests.

We used SMATR (Standardised Major Axis Tests & Routines, Version 2) [49], [50] to test for differences in the relationship between head width and body mass between stands of different ages and ants ascending and descending trees. When slopes were not different, we also tested for differences in the elevation and position of regression lines. We used the step down Bonferroni method of Holm to correct for multiple comparisons within each analysis (ANOVAS for sugars and amino acids, U-tests for aphid abundances and SMATR-analyses) [47], [51].


Effects of stand age on honeydew composition

We found 132 compounds in our honeydew samples, including 20 carbohydrates, seven amino acids, nine organic acids, fatty acids, a mineral acid and 85 unidentified compounds. Identified compounds that were not used in our analysis are listed in Table S1. We found no significant differences in the total composition of honeydew or in the composition of amino acids among stands of different ages. For carbohydrates there was a trend of different composition in clear cuts compared with old stands (PERMANOVA, Table 1). However, when the identified sugars and amino acids were analysed separately we found that the concentration of trehalose was smaller in clear-cuts than in middle-aged and mature stands. Similar, non-significant trends could be seen for sucrose, raffinose and melezitose (ANOVA, Table 2). Among amino acids, clear-cuts had the highest concentration of serine, mature stands were intermediate and middle-aged stands had the lowest concentration. A similar, but non-significant trend was detected for glutamine (ANOVA, Table 2). After corrections for multiple comparisons none of the trends for sugars and amino acids were significant. However, the Bonferroni correction procedure is often thought to be overly conservative [52], [53].

Table 1. Results from PERMANOVA comparing the chemical composition of honeydew harvested by Formica aquilonia among stands of different ages.

Table 2. F-values, and significance of mixed model ANOVA testing the effect of stand age on honeydew composition and mean ± SE for sugars and amino acids in honeydew harvested by Formica aquilonia in stands of different ages.

In the aphid survey, we sampled in total 2108 aphids from spruce trees with honeydew harvesting ants present. The samples were dominated by Cinara piceicola (1641 specimens) and Cinara pruinosa (164 specimens). Four specimens could not be determined and 299 were determined as Cinara sp. Both determined Cinara species were more abundant in clear cuts compared with middle aged and old stands but the pattern was only significant for C. piceicola (Kruskal-Wallis test, p = 0.018). The quota of C. pruinosa/C. piceicola did not differ among stand types (Kruskal-Wallis test, p = 0.883) but C. piceicola dominated the samples in clear cuts (quota 0.07±0.04, mean±SE) and C. pruinosa in old stands (quota 5.33±5.33, mean±SE), middle aged stands were intermediate (quota 0.88±0.82, mean±SE).

Effects of body size and stand age on forager mass

Ants descending trees were laden and thus heavier than ants ascending trees for all stand ages. The slope of the regression of body mass on head width was significantly lower for ants ascending than ants descending trees for stands of all ages (Table 3, Figure 1). This suggests that ants with larger heads carry more honeydew relative to their mass and may therefore be more efficient. For both ascending and descending ants, there were no differences in slope between stand ages.

Figure 1. Relationship between body mass and head width for ants ascending and descending trees in stands of different ages.

Line equations are: descending ants: clear-cut: y = −0.015+0.015x, R2 = 0.65; middle-aged: y = −0.015+0.015x, R2 = 0.64; mature: y = −0.017+0.015x, R2 = 0.57; ascending ants: clear-cut: y = −0.012+0.012x, R2 = 0.73; middle-aged: y = −0.011+0.012x, R2 = 0.71; and mature: y = −0.012+0.012x, R2 = 0.80.

Table 3. Test-statistic and significance from the SMATR analysis comparing the slopes of lines for the relationship between head width and body mass for Formica aquilonia workers ascending and descending trees.

We also tested for differences in the elevation of lines with equal slopes, i.e., within the groups of ascending and descending ants. For ascending ants, line elevation differed significantly between stands of different ages (Wald statistic(2) = 24.0, p<0.001), with elevation being highest in mature stands (Figure 1). This suggests that ants in mature stands are heavier relative to head width than those in other stand ages. Line position for ascending ants was not affected significantly by stand age (Wald statistic(2) = 4.4, p = 0.110).

For descending ants, line elevation differed significantly between stands of different ages (Wald statistic(2) = 10.1, p = 0.006) and was significantly lower in clear-cuts than in other stand ages (Figure 1), while line position did not differ between stands of different ages (Wald statistic(2) = 4.0, p = 0.134). This suggests that ants on clear-cuts may harvest slightly less honeydew in proportion to their head width.


Honeydew composition

Both sugar and amino acid concentrations tended to differ between stands of different ages, indicating that the quality of honeydew changes in response to forest management. Trends were similar for both univariate and multivariate analyses. The concentration of several sugars was lowest in clear-cuts. This trend was significant only for the disaccharide trehalose and only before corrections for multiple comparisons. Trehalose is the blood sugar of insects and typically makes up 30–35 percent of the honeydew sugar content [20], but is also found in the haemolymph of ants [54]. The origin of the trehalose in our samples is most probably honeydew because cloudy samples representing contamination with haemolymph were not used in the analysis. The nutritional value of trehalose relative to other sugars is unclear, but lower concentrations of trehalose and other sugars in honeydew on clear-cuts may contribute to the reduced success of F. aquilonia.

Raffinose, sucrose, and melezitose showed a similar trend to trehalose. Sucrose is nutritionally important for ants [55], [56], but the value of melezitose, which commonly makes up 50–60 percent of honeydew sugars, is unclear [20], [57]. Mutualist aphids increase the melezitose content of honeydew when tended [58], possibly because melezitose indicates the presence of sugar rich honeydew to ants (e.g. Lasius niger on Tanacetum vulgare, Germany) [22]. Although melezitose has been reported to be of nutritional value to some ants [59], other studies suggest that it is of low nutritional value to most insects [60] and can even be toxic [61], so may be merely tolerated by ants [56]. The sugar content of honeydew in combination with the presence of melezitose may thus be the critical factor in determining the extent of ant-attendance in aphids [62]. If melezitose is produced in response to ant tending, lower concentrations of melezitose on clear-cuts may indicate that aphids are attended less frequently by ants than in other stand ages. Ant activity on trees on clear-cuts is low relative to mature forests, yet aphids are extremely abundant on saplings in clear-cuts [31], suggesting that aphids may indeed be tended less in these sites.

In addition to sugars frequently observed in honeydew from aphids, our chemical analyses with GC-TOFMS identified several additional sugars e.g. nigerose and palatinose (Table 2), but they did not differ in concentrations among stand types. As we don't know the absolute concentrations of these sugars it is hard to estimate their relative importance. Further studies with this improved technology (GC-TOFMS) including measures of absolute concentrations are needed to reveal the function and relative importance of more unusual sugars in honeydew.

Concentrations of several amino acids were higher on clear-cuts than in older forests. Clear-cutting leads to increased availability of nitrogen in the soil for several years after cutting [63], [64] and soil scarification further speeds up this effect [65], [66]. Trees on clear cuts also contain more N in the needles than trees in older stands [67], so increased N-uptake by the trees after clear cutting may explain the increased amino acid content of aphid honeydew. Of the amino acids affected, serine is a major precursor to formic acid [68], so may be critical in colony defence behaviours, while glutamine is a storage protein for workers and reproductive castes [69]. Ant species that commonly collect nectar or honeydew may exhibit higher preferences for sources rich in proteins or amino acids [70]. This may reflect nitrogen limitation in their diet [71], which could be a result of decreases in prey availability after clear-cutting [72]. It is thus possible that increased nitrogen availability in honeydew on clear-cuts has positive effects on some aspects of ant biology.

The aphid surveys revealed that the ant tended Cinara pruinosa and Cinara piceicola dominated as honeydew producers in all stand types so it is highly probable that the collected honeydew arise from these two species. The numbers of aphids varied both among and within stands and both species often occurred on the same tree so it was impossible to know which species was the source of the honeydew. The higher abundance of both species on clear cuts might be a result of the sampling procedure since it was not possible to reach the tree crowns in middle aged and old stands. Although Cinara piceicola dominated the samples in clear cuts and C. pruinosa in old stands with middle aged stands intermediate the statistical analyses did not reveal a difference in the quota C. pruinosa/C. piceicola, probably because the low sample size in old stands. Honeydew composition differs among aphid species but also within species e.g. depending on host plant and ant attendance [58]. Because the same species of ant-attended aphids dominated in all stand ages in this study, and honeydew was collected from ants that highly probably had harvested their honeydew from aphid-colonies tended by the ants, differences in honeydew composition are likely to depend on site factors rather than differences in the source of honeydew.

Determinants of honeydew harvest by individual workers

Head width-mass slopes were steeper for descending than ascending ants, indicating that large ants harvested more honeydew than small ants. Ascending ants in mature forests weighed more for their size, suggesting that they may have been in better condition than ants in younger stands. However, they did not harvest more honeydew than ants in other stand ages. Both ascending and descending ants in clear-cuts weighed less than those in middle-aged and mature forests. Consistent with our findings, Sorvari and Hakkarainen (2009) showed that Formica aquilonia worker size, body fat-content and worker-generated nest temperature all decrease in response to clear-cutting. Previous studies suggest that food availability may determine the size of ant workers [24], [73] and that large workers may be superior foragers and defenders of nests [26], [74]. However, differences in the mass gain of ants between stands of different ages at these study sites were small and non-significant [31], even with a large sample size, so consequences for the colony are difficult to determine.

Despite suggestions that honeydew limitation is responsible for the decline of wood ants after clear-cutting [25], [29], [75], results from a previous study in the same stands show that in clear-cuts, ants harvest 77% of the honeydew mass that they harvest in mature stands [31]. This is probably a result of the high abundance of seedlings with high aphid loads in clear-cuts, which may compensate for the lack of mature trees. We thus suggest that changes in honeydew composition after clear-cutting may also play an important role in the inferior worker condition on clear-cuts.

Implications for conservation

This is the first study to show that honeydew quality is affected by anthropogenic disturbances. It suggests that changes in resource quality resulting from clear-cutting cascade through food chains. This may be particularly important for closely interacting species, such as those involved in mutualisms. We suggest that the reported poorer condition of F. aquilonia on clear-cuts is the result of changes in honeydew quality. Changes in food quality may thus exacerbate the changes in resource quantity and microclimate reported in previous studies [31], [35] and thus explain reported reductions in size and abundance of Formica aquilonia mounds following clear-cutting. Other honeydew-dependent organisms, such as microbes, may also be affected by this change in quality [76], [77]. Thus, changes in honeydew quality due to forestry may have further consequences for species and ecosystem functions beyond those reported here.

Supporting Information

Table S1.

Mean and SE for chemical compounds in honeydew harvested by Formica aquilonia in different stand ages. Concentrations are presented in kilo area counts as retrieved from the GC/MS analysis (K area counts). Data for the sugars and amino acids that were used in the statistical analyses are shown in Table 2.



We thank Krister Lundgren for performing the chemical analyses and Thomas Moritz for help with identification of compounds. Nils Eriksson determined the aphids. Ylva Nordström assisted in the field.

Author Contributions

Conceived and designed the experiments: HG TJ. Performed the experiments: TJ HG. Analyzed the data: TJ HG. Contributed reagents/materials/analysis tools: TJ HG. Wrote the paper: TJ HG.


  1. 1. Grove SJ (2002) Saproxylic insect ecology and the sustainable management of forests. Annual Review of Ecology and Systematics 33: 1–23.
  2. 2. Harrison S, Bruna E (1999) Habitat fragmentation and large-scale conservation: what do we know for sure? Ecography 22: 225–232.
  3. 3. Zanette L, Doyle P, Tremont SM (2000) Food shortage in small fragments: Evidence from an area-sensitive passerine. Ecology 81: 1654–1666.
  4. 4. Akasaka M, Takamura N, Mitsuhashi H, Kadono Y (2010) Effects of land use on aquatic macrophyte diversity and water quality of ponds. Freshwater Biology 55: 909–922.
  5. 5. J. KrzyzanowskiPL Almuedo 2010 Cumulative impacts of natural resource development on ecosystems and wildlife: an annotated bibliography for British Columbia. FORREX Series. v + 43
  6. 6. Kareiva P (1987) Habitat fragmentation and the stability of predator prey interaction. Nature 326: 388–390.
  7. 7. Kruess A, Tscharntke T (1994) Habitat fragmentation, species loss, and biological control. Science 264: 1581–1584.
  8. 8. Didham RK, Ghazoul J, Stork NE, Davis AJ (1996) Insects in fragmented forests: a functional approach. TREE 11: 255–260.
  9. 9. Cunningham SA (2000) Depressed pollination in habitat fragments causes low fruit set. Proceedings of the Royal Society B: Biological Sciences 267: 1149–1152.
  10. 10. Pauw A (2007) Collapse of a pollination web in small conservation areas. Ecology 88: 1759–1769.
  11. 11. Gibb H, Cunningham SA (2009) Does the availability of arboreal honeydew determine the prevalence of ecologically dominant ants in restored habitats? Insectes Sociaux 56: 405–412.
  12. 12. Blüthgen N, Fiedler K (2004) Competition for composition: Lessons from nectar-feeding ant communities. Ecology 85: 1479–1485.
  13. 13. Davidson DW, Cook SC, Snelling RR, Chua TH (2003) Explaining the abundance of ants in lowland tropical rainforest canopies. Science 300: 969–972.
  14. 14. Davidson DW (1998) Resource discovery versus resource domination in ants: a functional mechanism for breaking the trade-off. Ecological Entomology 23: 484–490.
  15. 15. Cook SC, Davidson DW (2006) Nutritional and functional biology of exudate-feeding ants. Entomologica Experimentalis et Applicata 118: 1–10.
  16. 16. Way MJ (1958) The influence of other ant species on biological control of Oecophylla longinoda (Latr). Proceedings of the Xth International Congress of Entomology 4: 595–596.
  17. 17. Room PM (1975) Relative distributions of ant species in cocoa plantations in Papua New Guinea. Journal of Applied Ecology 12: 47–61.
  18. 18. Styrsky JD, Eubanks MD (2007) Ecological consequences of interactions between ants and honeydew-producing insects. Proceedings of the Royal Society B - Biological Sciences 274: 151–164.
  19. 19. Blüthgen N, Gebauer G, Fiedler K (2003) Disentangling a rainforest food web using stable isotopes: dietary diversity in a species-rich ant community. Oecologia 137: 426–435.
  20. 20. Hölldobler B, Wilson EO (1991) The Ants. Berlin: Springer-Verlag.
  21. 21. Blüthgen N, Gottsberger G, Fiedler K (2004) Sugar and amino acid composition of ant-attended nectar and honeydew sources from an Australian rainforest. Austral Ecology 29: 418–429.
  22. 22. Woodring J, Wiedemann R, Fischer MK, Hoffman KH, Völkl W (2004) Honeydew amino acids in relation to sugars and their role in the establishment of ant-attendance hierarchy in eight species of aphids feeding on tansy (Tanaceum vulgare). Physiological Entomology 29: 311–319.
  23. 23. Völkl W, Woodring J, Fischer M, Lorenz MW, Hoffman KH (1999) Ant-aphid mutualisms: the impact of honeydew production and honeydew sugar composition on ant preferences. Oecologia 118: 483–491.
  24. 24. Clémencet J, Doums C (2007) Habitat-related microgeographic variation of worker size and colony size in the ant Cataglyphis cursor. Oecologia 152: 211–218.
  25. 25. Sorvari J, Hakkarainen H (2009) Forest clear-cutting causes small workers in polydomous wood ant Formica aquilonia. Annales Zoologici Fennici 46: 431–438.
  26. 26. Evison SEF, Ratnieks FLW (2007) New roles for majors in Atta leafcutter ants. Ecological Entomology 32: 451–454.
  27. 27. Berg Å, Ehnström B, Gustavsson L, Hallingbäck T, Jonsell M, et al. (1994) Threatened plant, animal and fungus species in Swedish forests: Distribution and habitat associations. Conservation Biology 8: 718–731.
  28. 28. Thor G (1998) Red-listed lichens in Sweden: habitats, threats, protection, and indicator value in boreal coniferous forest. Biodiversity and Conservation 7: 59–72.
  29. 29. Punttila P, Haila Y, Pajunen T, Tukia H (1991) Colonization of clear-cut forests by ants in the southern Finnish taiga - a quantitative survey. Oikos 61: 250–262.
  30. 30. Kilpeläinen J, Punttila P, Finér L, Niemelä P, Domisch T, et al. (2008) Distribution of ant species and mounds (Formica) in different-aged managed spruce stands in eastern Finland. Journal of Applied Entomology 132: 315–325.
  31. 31. Gibb H, Johansson T (2010) Forest succession and harvesting of hemipteran honeydew by boreal ants. Annales Zoologici Fennici 47: 99–110.
  32. 32. Sorvari J, Hakkarainen H (2007) Wood ants are wood ants: deforestation causes population declines in the polydomous wood ant Formica aquilonia. Ecological Entomology 32: 707–711.
  33. 33. Sorvari J, Hakkarainen H, Rantala MJ (2008) Immune defense of ants is associated with changes in habitat characteristics. Environmental Entomology 37: 51–56.
  34. 34. Sorvari J, Hakkarainen H (2005) Deforestation reduces nest mound size and decreases the production of sexual offspring in the wood ant Formica aquilonia. Annales Zoologici Fennici 42: 259–267.
  35. 35. Domisch T, Finér L, Neuvonen S, Niemelä P, Risch AC, et al. (2009) Foraging activity and dietary spectrum of wood ants (Formica rufa group) and their role in nutrient fluxes in boreal forests. Ecological Entomology 34: 369–377.
  36. 36. Rosengren R, Sundström L (1991) The interaction between red wood ants, Cinara aphids, and pines. A ghost of mutualism past? In: Huxley CR, Cutler DF, editors. Ant-Plant interactions. Oxford: Oxford University Press. pp. 80–91.
  37. 37. Ahti T, Hämet-Ahti L, Jalas J (1968) Vegetation zones and their sections in northwestern Europe. Annales Botanici Fennici 5: 169–211.
  38. 38. Collingwood CA (1979) The Formicidae (Hymenoptera) of Fennoscandia and Denmark. Klampenborg, Denmark: Scandinavian Science Press Ltd.
  39. 39. Savolainen R, Vepsäläinen K, Wuorenrinne H (1989) Ant assemblages in the taiga biome: testing the role of territorial wood ants. Oecologia 81: 481–486.
  40. 40. Punttila P (1996) Succession, forest fragmentation, and the distribution of wood ants. Oikos 75: 291–298.
  41. 41. Gullberg J, Jonsson P, Nordström A, Sjöström M, Moritz T (2004) Design of experiments: an efficient strategy to identify factors influencing extraction and derivatization of Arabidopsis thaliana samples in metabolomic studies with gas chromatography/mass spectrometry. Analytical Biochemistry 331: 283–295.
  42. 42. Ltd P-E (2007) Primer 6.2.1. Plymouth, UK: PRIMER-E Ltd.
  43. 43. Anderson MJ (2003) NPMANOVA: a FORTRAN computer program for non-parametric multivariate analysis of variance (for any two-factor ANOVA design) using permutation tests. New Zealand: Department of Statistics, University of Auckland.
  44. 44. Clarke KR (1993) Non-parametric multivariate analyses of changes in community structure. Australian Journal of Ecology 18: 117–143.
  45. 45. Field JG, Clarke KR, Warwick RM (1982) A practical strategy for analysing multispecies distribution patterns. Marine Ecology Progress Series 8: 37–52.
  46. 46. Anderson MJ, Gorley RN, Clarke KR (2008) PERMANOVA+ for PRIMER: Guide to Software and Statistical Methods. Plymouth, UK: PRIMER-E.
  47. 47. SAS Institute I (2003) SAS. 9.1 ed. Cary, NC: SAS Institute, Inc.
  48. 48. SAS Institute I (2008) JMP 8. Cary, NC: SAS Institute, Inc.
  49. 49. Falster DS, Warton DJ, Wright IJ (2006) SMATR: Standardised major axis tests and routines, Version 2 SMATR website. Available: Accessed 2009 Jun 12.
  50. 50. Warton DJ, Wright IJ, Falster DS, Westoby M (2006) Bivariate line-fitting methods for allometry. Biological Reviews 81: 259–291.
  51. 51. Rice WR (1989) Analyzing tables of statistical tests. Evolution 43: 223–225.
  52. 52. Cabin RJ, Mitchell RJ (2000) To Bonferroni or not to Bonferroni: when and how are the questions. Bulletin of the Ecological Society of America 81: 246–248.
  53. 53. Garcia J (2004) Escaping the Bonferroni iron claw in ecological field studies. Oikos 105: 657–663.
  54. 54. Schilman PE, Roces F (2008) Haemolymph sugar levels in a nectar-feeding ant: dependence on metabolic expenditure and carbohydrate deprivation. Journal of Comparative Physiology B 178: 157–165.
  55. 55. Warner J, Scheffrahn RH (2004) Feeding preferences of white-footed ants, Technomyrmex albipes (Hymenoptera: Formicidae), to selected liquids. Sociobiology 44: 403–412.
  56. 56. Blüthgen N, Fiedler K (2004) Preferences for sugars and amino acids and their conditionality in a diverse nectar-feeding ant community. Journal of Animal Ecology 73: 155–166.
  57. 57. Fischer MK, Völkl W, Schopf R, Hoffman KH (2002) Age-specific patterns in honeydew production and honeydew composition in the aphid Metopeurum fuscoviridae: implications for ant-attendance. Journal of Insect Physiology 48: 319–326.
  58. 58. Fischer MK, Shingleton AW (2001) Host plant and ants influence the honeydew sugar composition of aphids. Functional Ecology 15(4): 544–550.
  59. 59. Detrain C, Verheggen FJ, Diez L, Wathelet B, Haubruge E (2010) Aphid-ant mutualism: how honeydew sugars influence the behaviour of ant scouts. Physiological Entomology 35: 168–174.
  60. 60. Wäckers FL (1999) Gustatory response by the hymenopteran parasitoid Cotesia glomerata to a range of nectar and honeydew sugars. Journal of Chemical Ecology 25: 2863–2877.
  61. 61. Zoebelein G (1956) Der Honigtau als Nahrung der Insekten, Teil I. Zeitschrift für Angewandte Entomologie 38: 369–416.
  62. 62. Fischer MK, Völkl W, Hoffman KH (2005) Honeydew production and honeydew sugar composition of polyphagous black bean aphid, Aphis fabae (Hemiptera: Aphididae) on various host plants and implications for ant-attendance. European Journal of Entomology 102: 155–160.
  63. 63. Ring E (1996) Effects of previous N fertilizations on soil-water pH and N concentrations after clear-felling and soil scarification at a Pinus sylvestris site. Scandinavian Journal of Forest Research 11: 7–16.
  64. 64. Piirainen S, Finér L, Mannerkoski H, Starr M (2002) Effects of forest clear-cutting on the carbon and nitrogen fluxes through podzolic soil horizons. Plant and Soil 239: 301–311.
  65. 65. Smolander A, Heiskanen J (2007) Soil N and C transformations in two forest clear-cuts during three years after mounding and inverting. Canadian Journal of Soil Science 87: 251–258.
  66. 66. Smolander A, Paavolainen L, Mälkönen E (2000) C and N transformations in forest soil after mounding for regeneration. Forest Ecology and Management 134: 17–28.
  67. 67. Sah SP, Ilvesniemi H (2006) Effects of clear-cutting and soil preparation on natural N-15 abundance in the soil and needles of two boreal conifer tree species. Isotopes in environmental and health studies 42: 367–377.
  68. 68. Hefetz A, Blum MS (1978) Biosynthesis of formic acid by the poison glands of Formicinae ants. Biochimica et Biophysica Acta 543: 484–496.
  69. 69. Wheeler Q, Martinez T (1995) Storage proteins in ants (Hymenoptera: Formicinae). Comparative Biochemistry and Physiology 112B: 15–19.
  70. 70. Kay A (2002) Applying optimal foraging theory to access nutrient availability ratios for ants. Ecology 83: 1935–1944.
  71. 71. Yanoviak SP, Kaspari M (2000) Community structure and the habitat templet: ants in the tropical forest canopy and litter. Oikos 89: 259–266.
  72. 72. Atlegrim O, Sjöberg K (1995) Effects of clear-cutting and selective felling in Swedish Boreal coniferous forest: Response of invertebrate taxa eaten by birds. Entomologica Fennica 6: 79–90.
  73. 73. Johnson RA (2002) Semi-claustral colony funding in the seed-harvester ant Pogonomyrmex californicus: a comparative analysis of colony funding strategies. Oecologia 132: 60–67.
  74. 74. Rosengren R, Cherix D, Pamilo P (1985) Insular ecology of the red wood ant Formica truncorum 1. Polydomous nesting population size and foraging. Mitteilungen der Schweizerischen Entomologischen Gesellschaft 58: 147–176.
  75. 75. Domisch T, Finer L, Jurgensen MF (2005) Red wood ant mound densities in managed boreal forests. Annales Zoologici Fennici 42: 277–282.
  76. 76. Stadler B, Müller T (1996) Aphid honeydew and its effect on the phyllosphere microflora of Picea abies (L) Karst. Oecologia 108: 771–776.
  77. 77. Michelsen A, Graglia E, Schmidt IK, Jonasson S, Sleep D, et al. (1999) Differential responses of grass and a dwarf shrub to long-term changes in soil microbial biomass C N and P following factorial addition of NPK fertilizer fungicide and labile carbon to a heath. New Phytologist 143: 523–538.