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However, this influence is strongly dependent on the disturbance rate, pointing to an important interaction between spatial structure and disturbance.
The composition of the landscape is a reflection of the balance between the disturbance rate and successional development.
We adjust the rate of such disturbance events in such a way that the per-site disturbance rate is held fixed.
The former are not so surprising, given that they combine to produce an overall disturbance rate, but the latter shows that the resulting impact on age-class structure can be influenced to some degree through management objectives.
We found that increasing the spatial scale of disturbances (while keeping the overall disturbance rate fixed) can increase population density, but generally only when landscape turnover is slow relative to population dynamics and when the population is somewhat close to its extinction threshold.
To lower the probability of occurrence of such catastrophic ecosystem shifts, harvesting rate must decrease when fire frequency increases (Bergeron et al. 2006; Raulier et al. 2013), so that the total disturbance rate (harvesting + wildfire) does not exceed the maximum disturbance rate recorded during the Holocene.
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At the continental scale, regional differences in disturbance rates reflect management patterns of high disturbance rates in the Southeastern and South Central states, and lower disturbance rates in the Northeast and Northern Lakes States.
Consequently, national disturbance rates greatly increased by 2000, and remained high for much of the decade.
During the first part of the time series, national disturbance rates largely reflected trends in harvest disturbance.
Although low compared to harvest and decline, fire disturbance rates also increased in the early- to mid-2000s.
We used multi-temporal remote sensing data to assess landscape-scale changes in disturbance rates, patch size and age structure.
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