Let’s look some more at thinning.
First, I’ll say that I don’t know about wet areas. I remember a class at an Area 4 Silviculture Workshop in the 80’s, taught by Chad Oliver and Bruce Larsen (then of U of Washington). All the models were based on competition for light. I asked “but what if the trees are competing for water?”. That wasn’t part of modeling at the time. So much of forest ideas and models were generated from wet forests and don’t apply to dry forests. The point being that any discussion of thinning needs to be grounded in specifics of when, where and why.
At one end we have “no thinning is ever ecologically necessary.” Well, that’s a high bar, and not one that’s in law anywhere as I know for activities on National Forests. I don’t know that campgrounds or ski areas are ecologically necessary either. So the term “ecologically necessary” has to carry quite a bit of weight, especially if different fuels-related assumptions are involved. Are fuels prescriptions ecological? What if the fuels practitioner is trained as a fire ecologist? What do we mean by the term “ecological” in that sense?
Anyway, I’ll make a series of claims that we can discuss.
1. Thinning in forests is very common, at least here in Colorado, outside of a wood products context – purely for fuel treatment or wildfire mitigation. Then there are the folks in Arizona and the Lake Tahoe area, trying to find and encourage wood products companies to take their thinned material.
2. Some people thin in dry areas to reduce density of trees, because more trees can get started than the site can ultimately support. Thinning gives the remaining trees a better chance to get enough water to grow.
3. Some people thin (at least in California) to return to HRV (with the side benefits of fewer stems on health and resilience as above.)
4. Healthier trees (with stem reduction) are often, but not always, more resistant to bark beetles.
5. Removing biomass (cutting trees and removing them from the site by burning or other removal) reduces fuels.
6. Thinning can be done to help trees grow larger faster, as with west side plantations trying to get bigger trees for habitat, or in many places for wood products.
7. Some species, in some situations, have a tendency to stagnate rather than develop into stands such that without thinning trees don’t become large (“doghair”)..
To engage with previous comments:
Jon said:
It looks like this was looking at basal area rather than the size of trees removed, so I don’t think it proves the point that removing large trees is necessary to protect large trees from drought (or fires?) – unless large trees are all that were growing here.
Yes, I would say if all trees are large in a stand are large, and you want to thin, you would need to remove some large trees.
Jon also said in an earlier comment:
we should minimize it and be choosy about where that is done. Not to mention clearly explaining all this in the rationale for a project. This is what I’m not seeing discussed.
As we shall see in the next post, at least some environmental documents do have rationales and different ways of monitoring “choosiness” have been proposed.
Jake had some interesting comments:
While mortality from MPB was significantly less in the thinned areas (3% vs 13%), when the trees killed by the thinning (which also removed infested living trees) were included in mortality, total mortality is much greater in the thinned areas.
Let’s think about this some more.. (I didn’t go back and look at the study). When the thinning occurred, they removed more trees than might have been killed by beetles. But the way the stand develops, with more standing and falling dead trees (with MPB death) would be different, and more fuel would be in the stand. I’m not sure that those prescriptions were intended to reduce fuel loadings at the time, but I think it would be hard to argue that such a prescription would not reduce fuel loads.
Is that really “shady accounting” as Jake states? If the goal is to reduce MPB kill, then thinning would generally be successful. That would be in the framing of the study itself (reduce MPB mortality) rather than (how to maximize living trees on a site).
Also, the Negron et al (2017) study reported that 4 of their 21 thinned stands had much greater MPB mortality than the paired unthinned stands
That’s the “it doesn’t always work” argument. We’ve discussed that before with regards to fuel treatments in general.
Another of Jake’s comments:
Thinning, of course, had the benefit of providing saw logs to the mill, but it also probably came with significant costs to the ecosystem.
“Costs to the ecosystem” “ecologically necessary”. I thought the “ecological integrity” part of the 2012 Planning Rule suggested managing for NRV- related to HRV. But not if HRV is too open or requires thinning. It’s all very confusing.
Instead of “ecological integrity” perhaps the FS should have targeted “forest resilience” which would definitely have a fuels (both for the trees on-site and to support suppression via PODs and other fuelbreaks.
But what “costs to the ecosystem” come from thinning specifically? Wouldn’t it depend on when, where and why?
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