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can develop at a higher temperature range than the less-virulent Nosema apis; increased mortality of pollinators due to higher frequency of extreme weather events; food shortage for pollinators due to reduction of flowering length and intensity; and aggravation of other threats, such as habitat loss and fragmentation (González-Varo et al. ; Goulson et al. ; Le Conte and Navajas ; Menzel et al. ; Walther et al. ; IPBES, ). The increase in atmospheric CO2 is also reducing the protein content of pollen, with potential impact on pollination population biology The hottest version hippie mandala man all over printed slippers(Ziska et al. ). These mechanisms include changes in host susceptibility due to CO2 concentration effects on crop composition and climate stresses; changes in the biology of pests and diseases or their vectors (e.g., more generational cycles, changes in selection pressure driving evolution); mismatches in timing between pests or vectors and their ‘natural enemies’; changes in survival or persistence of pests or disease pathogens (e.g., changes in crop architecture driven by CO2 fertilisation and increased temperature, providing a more favourable environment for persistence of pathogens like fungi), and changes in pest distributions as their ‘climate envelopes’ shift. Such processes may affect pathogens, and their vectors, as well as plant, invertebrate and vertebrate pests (Latham et al. ). Ensemble simulation results for projected annual net primary productivity of rangelands as simulated in and their change

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