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in EcologyFairy circles in Namibia are assembled from genetically distinct grasses
Fairy circles (FCs) are remarkably circular and regular vegetation patterns covering an area of thousands of square kilometres in hyper-arid grasslands in Southern Africa (e.g. Namibia)1,2,3. They are typically made up of perennial tufts of Stipagrostis grass growing around barren circular patches roughly 2–10 m in diameter, with annual or perennial grasses in the area between circles, the matrix1,2. The edges of FCs are about 5–10 m apart and when dense they have a regular hexagonal arrangement3. Similar vegetation rings also occur in arid lands in Australia, Israel and elsewhere1,2,3,4,5,6,7. The processes leading to the formation of FCs have been the subject of debate for several decades8,9,10,11,12,13.
Aspects of FCs that require explanation include how and why individual circles form, how they persist and how the similar size and regular pattern is established at the landscape scale. The bare centres of individual FCs persist in situ almost permanently, although the peripheral plants delimiting the circles are much shorter-lived. Van Rooyen et al.8 noted no change in the position of five marked FCs over 22 years, despite intervening droughts8. Tschinkel14 analysed pairs of aerial photographs taken 4 years apart, and on the basis of how many FC positions were unchanged, died or emerged, estimated that average sized FCs persist in situ for an average of 75 years, implying some circles remain in situ for a century14. Similarly, using aerial photographs, Juergens2 noted a high survival (97%) of FCs in situ over a 50-year period (=0.06% pa mortality), implying an age of millennia for some FCs2.
Many alternative hypotheses have been proposed for FC spatial and temporal patterns, but without agreement. The first hypothesis is based on ecosystem engineering by termites that remove plants from the centres of circles2, facilitating localized underground water accumulation in circle centres. This moisture maintains the termites and the band of perennial grass on which termites feed year-round. The spatial patterning of the FCs is considered to result from competition between termite colonies2. However, the poor correlation of FCs with the presence of specific termites is an important concern with this hypothesis13.
The second hypothesis is based on the clonal mode of growth of individuals of many arid-land species that create vegetation rings4,6,7,15. For example, rings are formed by one of the Namibian FC species, Stipagrostis ciliata in the Negev desert. Here individual plants of this species send out underground rhizomes, which, with increasing age, results in a ring of ramets (i.e. sprouts from the same clonal colony or genet) around a barren central patch, which forms as the plant centre dies4. Such vegetation rings form and enlarge centrifugally due to competition between ramets, and as this process continues over time new ramets establish successfully only towards the periphery4,7. Globally, all of the many plant species that form circles do so by this type of clonal growth15. As the pattern of FCs is virtually fixed in situ for centuries, this suggests that the plants that indicate the pattern may also be long-lived. Individual clonal plants can be extremely long-lived15,16, which could then match longevities between the plants and the FCs they delimit. The clonality hypothesis could thus explain how circular shapes form (by self-thinning of ramets spreading from source plant), why bare centres occur (resource depletion and source plant death) and how they can persist over long periods of time (by continuous production of short-lived ramets). However, clonality has been disputed8 as an explanation for FCs for two reasons. Firstly, van Rooyen et al. suggested that the FCs referred to by Danin and Orshan are considerably smaller (about 2 m) than most FCs in Namibia4,8. Although this is correct that FCs tend to be much larger in Namibia, the mean size of FCs can be as small as 2.5 m in some areas2. Secondly, van Rooyen and colleagues suggested that clonality cannot explain why FC centres are bare8. Bare centres are now well known in rings and are commonly explained as being due to inter-ramet competition and resource depletion7.
The third hypothesis for FC spatial patterns is that it emerges through vegetation self-organization (the VSO hypothesis)1,5,12,17,18. Grasses in the peripheral band outcompete grasses in the FC centre and keep it bare and moist at depth1. The plants in the peripheral bands also compete with the matrix grasses and with the peripheral bands on adjacent FCs to maintain the regular pattern1. Mathematical vegetation models based on partial differential equations represent the theoretical basis of the VSO hypothesis17,18. These partial differential equations do not operate at the scale of individual-plant interactions, but at the level of local processes (largely rates of lateral water movement due to plant evapo-transpiration) in comparison to rates of lateral biomass spread. For these current VSO models, lateral water flow needs to be about 100 times faster than lateral biomass spread18. Thus, the mode and rate of how biomass spreads, whether via clonal growth or seed dispersal and population growth18, has an impact on the viability of vegetation-patterning models. In the absence of such information for FCs, the most recent VSO modelling study18 assumed a rate of biomass dispersal (1.2 m2 yr−1) derived from the Canadian woodlands19, for clonal spread or seed dispersal. These literature values may be unrealistic for FCs. For example, 1.2 m2 yr−1 is likely to be too high for clonal growth in the arid circumstances in which FCs occur. Stipagrostis individual plants across the landscape are typically only 0.005–0.13 m2 in canopy area with a mean area of 0.05 m2 (ref. 20). Similarly, clonal spread in other systems can also be lower than 1.2 m2 yr−1 by orders of magnitude (ref. 19). Alternatively, if Stipagrostis plants are not clones, their highly awned seeds will disperse much further than 1.2 m2 yr−1. Finally, if the assumed 1.2 m2 yr−1 biomass spread18 is due to the total growth of new recruits per parent individual, then this implies unrealistically high population growth rates ( >20 new recruits, each with 0.05 m2 in canopy volume20 required per parent individual). Getzin et al.3 acknowledge that in the context of their VSO model it needs to be further investigated whether grass tufts experience a central dieback due to self‐thinning, i.e. the role of clonality33. Thus, clonality may be relevant to some VSO models.
Juergens has argued that there is a spatial mismatch in the root length and inter-FC distances10 and therefore that FCs cannot directly interact with each other to produce the regular spatial pattern. An extreme example of this mismatch is a study by Ravi et al. reporting that the roots of peripheral plants in FCs had a mean length of 5.9 cm, which is more than two orders of magnitude shorter than inter-circle distances (10–20 m)12. These short root lengths would make competition for water and other resources over long distances crucial for explaining FC patterning1. Most recently, Ravi et al.12 rejected the termite hypothesis due to an absence of termites and partially invoked clonal dynamics as well as the VSO to explain their FC patterning12.
In summary, there are critical issues with all the hypotheses explaining the formation of FCs and the role of clonality appears to be relevant to two of the hypotheses. Here, we use ddRAD-seq as a genetic test of clonality of peripheral grasses. Our analysis indicates that most individual grasses surrounding FCs are genetically distinct and does not support the clonality hypothesis. More200 Shares149 Views
in EcologyCharacteristics of temperature evolution from 1960 to 2015 in the Three Rivers’ Headstream Region, Qinghai, China
The spatiotemporal characteristics analysis
The temporal characteristics
As seen in Fig. 2a, the climate tendency rate of the annual mean temperature series is 0.337 °C per decade, and its correlation coefficient is 0.7674 ( > r0.01 = 0.3357). In conjunction with the result of the M–K trend test, this finding demonstrates that the annual mean temperature has significantly increased in the past 56 years. In addition, the climate tendency rates of the annual mean temperature in the LARHR, YERHR and YARHR are 0.352 °C per decade, 0.34 °C per decade and 0.319 °C per decade, respectively (except for the climate tendency rate of the annual temperature in the YARHR, the correlation coefficients of the annual temperature series exceeded the significance level of 0.01). These rates exceed the mean rising rate of annual mean temperature in China (0.21–0.25 °C per decade) and that of the global annual mean temperature (0.07℃ per decade) in the past 56 years. The climate tendency rates of the annual mean temperature in the LARHR and YERHR were higher than those in Northwest China (0.32 °C/10a)1,27, and the climate tendency rate of the annual mean temperature in the YARHR was similar to that in Northwest China. The higher annual climate tendency rate of the THRHR is related to the increase in the lowest night temperature in the study area28 and the large amount of solar radiation in the lower altitude area of the THRHR13; furthermore, it may also be related to the decrease in total cloud cover and the increase in snow cover in the study area29. In addition, as seen in Fig. 2a,b, the annual mean temperature of the THRHR has increased significantly since the late1990s.
Figure 2The change in annual mean temperature in the THRHR from 1960 to 2015.
Full size image
As seen in Fig. 3, the annual and seasonal mean temperatures in the THRHR and its three subregions have been increasing in fluctuations since the 1960s, and the fluctuations in winter and spring are greater than those of summer and autumn. Due to the higher climate tendency rate of the summer, autumn and winter in LARHR than in the other two subregions, the orders of the climate tendency rate of seasonal mean temperature in the THRHR are completely consistent with that of LARHR (autumn, summer, winter, and spring mean temperatures), which are different from that in Northwest China (winter, autumn, spring and summer mean temperatures). In the three subregions, the spring climate tendency rate is lowest, and the orders of the climate tendency rate of autumn and winter are higher than that of spring, while that of summer varies greatly, it is highest in the YARHR, and that of autumn in the LARHR and the YERHR are highest. The high temperature rise rate in autumn and winter in the THRHR is related to the increase in the lowest temperature at night, the climate high tendency rate of winter in three subregions corresponds with the positive phase of the Arctic Oscillation (AO), and namely, the high climate tendency rate of winter corresponds with the high value of the AO. In addition, the annual and seasonal mean temperatures in the LARHR are ≥ 0 °C, respectively; meanwhile, the increasing range of the seasonal mean temperature climate tendency rate is significantly higher than that in the YERHR and YARHR, respectively. The decadal mean temperatures, the decadal minimum and maximum temperatures and their extreme values in the YERHR are lower than those in the LARHR, while they are higher than those in the YARHR (the value of decadal mean temperature is More
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in EcologyBowhead whales use two foraging strategies in response to fine-scale differences in zooplankton vertical distribution
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