1998
DOI: 10.2307/1551978
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Global Change and Arctic Ecosystems: Conclusions and Predictions from Experiments with Terrestrial Invertebrates on Spitsbergen

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Cited by 121 publications
(90 citation statements)
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“…This probably relates to the most abundant species achieving their Table 5 Spearman's rank correlation coefficient (r S ) for density of Folsomia quadrioculata, Hypogastrura viatica and total collembolan density with distance from seabird colony (only data from the sampling plots from the two ornithogenically influenced transects included), and with each specific environmental factor examined (data from all sampling plots included) optimum occurrence at points below the maximum seabird influence (guano deposition), as suggested by Sømme and Birkemoe (1999). Our data are consistent with previous observations that springtail abundance is not directly dependent on a single factor but is likely related to a suite of complex environmental conditions, such as habitat moisture, temperature, acidity, organic matter content, vegetation cover, soil structure and composition (Hodkinson et al 1998;Herzberg et al 2000;Filser 2002;Cassagne et al 2003;Dollery et al 2006; Springtail distribution and density often reflect the patchy nature of their habitat, especially in earlier vegetation succession stages . Notwithstanding this influence of habitat, microarthropod distributions in polar soils and vegetation profiles are characteristically patchy or uneven, even in otherwise apparently uniform habitats (Usher andBooth 1984, 1986).…”
Section: Discussionsupporting
confidence: 92%
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“…This probably relates to the most abundant species achieving their Table 5 Spearman's rank correlation coefficient (r S ) for density of Folsomia quadrioculata, Hypogastrura viatica and total collembolan density with distance from seabird colony (only data from the sampling plots from the two ornithogenically influenced transects included), and with each specific environmental factor examined (data from all sampling plots included) optimum occurrence at points below the maximum seabird influence (guano deposition), as suggested by Sømme and Birkemoe (1999). Our data are consistent with previous observations that springtail abundance is not directly dependent on a single factor but is likely related to a suite of complex environmental conditions, such as habitat moisture, temperature, acidity, organic matter content, vegetation cover, soil structure and composition (Hodkinson et al 1998;Herzberg et al 2000;Filser 2002;Cassagne et al 2003;Dollery et al 2006; Springtail distribution and density often reflect the patchy nature of their habitat, especially in earlier vegetation succession stages . Notwithstanding this influence of habitat, microarthropod distributions in polar soils and vegetation profiles are characteristically patchy or uneven, even in otherwise apparently uniform habitats (Usher andBooth 1984, 1986).…”
Section: Discussionsupporting
confidence: 92%
“…In spite of widespread recognition of the important role of seabird colonies in enriching otherwise nutrient-poor polar terrestrial ecosystems (Smith 1979;Joly et al 1987;Ryan and Watkins 1989;Hodkinson et al 1994Hodkinson et al , 1998Byzova et al 1995;Uvarov and Byzova 1995;Sømme and Birkemoe 1999), qualitative and quantitative data documenting any consequential impacts on their soil invertebrate communities are still limited. The aims of this study were, therefore:…”
Section: Introductionmentioning
confidence: 99%
“…Two main factors are the short growing season and the low temperatures, which are especially pertinent for relatively thermophilous species that may only be able to set viable seeds in infrequent years of high summer temperatures (Sørensen 1941;Wookey et al 1995;Alsos et al 2003). Low temperatures also reduce pollinator activity (Hodkinson et al 1998) and drive the reproduction mode towards asexuality (Peck et al 1998), which may influence successful reproduction and seed set. Although some species reproduce with asexual (apomictic) seeds, many essentially rely on runners or bulbils for dispersal (Wehrmeister and Bonde 1977;Murray 1987;Dormann et al 2002).…”
Section: Introductionmentioning
confidence: 99%
“…These freeze-thaw cycles may reduce the winter survival of insects, either by ice-crust formation leading to anoxic conditions or by loss of cold-hardiness during an early melt period followed by further freezing (Hodkinson et al, 1998;Sinclair et al, 2003;Hodkinson, 2005;Turnock and Fields, 2005). With increasing summer temperatures, seasonal patterns of arthropod emergence may be altered or disrupted, especially in species with highly seasonal life cycles (Hodkinson et al, 1998). Changes in the phenology of summer emergence may affect the life cycles of the arthropods themselves (in either positive or negative ways), but they will also affect the seasonal pattern of food availability for birds (and other invertebrate predators), and possibly the optimal timing for breeding for these species.…”
Section: Introductionmentioning
confidence: 99%