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From what I've read, the proportion of snags was much larger in undisturbed (by humans) forests, but the stem densities were, in the types of habitats we're discussing, still lower than present. The only pictorial I can think of that illustrates this is in the book Exploring with Custer: The 1874 Black Hills Expedition. In it, 48 landscape photographs of the Black Hills taken by Illingsworth in 1874 are coupled with pictures taken sometime around 2000. The stem densities are plainly higher in the modern photos, and the standing dead wood component is visibly smaller (in some cases, much smaller), at the very least relative to the overall stem density. Of course, this is just qualitative comparison of photos, but quantitative comparisons are a little tough to do when the snags themselves decompose over time and aren't leaving pollen deposits or something else useful in determining their historic and pre-historic densities.
This should make some sense, because in the more fire-prone ecosystems with shorter fire return intervals, ground fires didn't burn hot enough to consume entire standing dead trees in a single session, and especially in pine forests, frequent ground fires cause the surviving trees to increase resin production that then makes the tree much more resistant to burning after it dies. Then too, red pine/white pine forests seem to have had fire return intervals on the order of 250-500 years, over which time considerable dead wood could accumulate and lead to mixed severity fires. Jack pine and black spruce forests, on the other hand, have much shorter fire return intervals and tend to burn as as running crown fires, not because they are overstocked with snags, but because their growth pattern provides abundant dead branches as fine fuel that runs from the ground right up to the top of the trees.
The standing dead component in the western forests now seems to be driven by mountain pine beetle infestations, which in turn are driven by an increase in minimum winter temperatures so that winter kill is no longer controlling outbreaks, and by extremely high stem densities created by an absence of fire during the control era. The beetles are going to run their course, that horse is out of the barn and over the horizon. As they run their course, they'll solve the stem density problem too. I think this particular problem is so far ahead of what any lumber company or group of companies could accomplish that some catastrophic fires are inevitable. The Forest Service and other land management agencies don't have the money or manpower to go out and selectively thin tens of millions of acres within a year or two...NEPA alone for a program like that could take several years. Even if these companies or agencies could do it, there is no economic return to them. What marketable products start with doghair pine stands and overgrown striped maple as raw material?
And as far as the big tree issue...I was thinking specifically of truly giant white pines (200+ feet), cypress, hemlock, redcedar, stuff like that. Trees like that, you're looking at 200 or more years for the white pine to reach that size, and for the other three to reach massive size, it's on the order of 500-700 years. Not so with something like a cottonwood, but then cottonwoods need to grow fast because they're prone to washouts in riparian areas. Also not so with pinon pine or bristlecone pine. I was focusing mainly on trees in forest types with longer fire return intervals.
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