Forest list archive: msg00093

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Re: Re Roundtable Discussion



>I'd like to reply to Brett's comment that management can be controlled, but
>natural disasters cannot.  First, not all disturbances are "disasters" and what
>is or is not a disaster has a strong anthropocentric component that is not
>within the scope of this discussion (or maybe it is - but I'll leave that to
>others to debate and stick to disturbances).  And some disturbances that might
>be classified as disasters are the result of management activities - some very
>well-intentioned, such as suppressing fires.
>
>  The 1994 Tyee Fire (Wenatchee NF) burned 142,000 acres.  The burn spanned
>vegetation from shrub-steppe to subalpine forest, but most of the area burned
>was in dry pine forest that  (excuse this - I don't know how to format the DG)
>
>historically burned every 3 to 6 years for the past 500 years (determined from
>tree ring analysis of wedges cut from these trees), with the exception of the
>last 100 years during which fires were suppressed.  The change to the natural
>disturbance regime, while initiated by timber interests, led to vegetation
>characteristics that made spotted owls (and many wildlife biologists and
>environmentalists) happy.  Open stands of pine were converted to multi-layered
>stands of pine, Douglas-fir and true firs.  Just before the fire, stands had a
>2 to 7 fold increase in density over historical conditions.  Fuels were
>connected vertically and horizontally across the landscape.  Yes, the weather
>conditions were somewhat anomolous - but over several centruies, the PNW DOES
>have those "blocking highs" in the Pacific that make for severe fire years.
>Anyway - the Tyee burned and so did 9 owl nests and the ecosystems that the
>nests were in.  The resulting landscape will not support owls for al long time
>(and maybe didn't historically...).
>
>All this background to explain why I think we need to evaluate inherent
>disturbance regimes *and the vegetation characteristics that resulted* before
>we determine through the courts just how big a clearcut should or shouldn't be.
>In some forests, perhaps clearcuts are not appropriate, but perhaps they ARE in
>other forests - some of our biodiveristy (not just game animals, but
>butterflies too) requires open areas.  And, this diversity evolved under
>vegetation characteristics that resulted from the disturbance regime.
>    By the way, the Hubbard Brook study you referred to indicated, I think,
>that about 3% of site nutrients were stored in the *boles* of trees - that part
>usually taken off-site during harvesting.  If branches, needles/leaves, bark
>can remain onsite (not at a landing) loss of nutrients is significantly
>reduced.  And the loss of nutrients by fire *can*  be very high - both from the
>burn itself (it goes into the atmosphere and doesn't remain on site) and from
>erosion following rain on devegetated slopes.  If you want to challenge
>harvesting effects, I suggest that soil compaction, not nutrient depletion, is
>a more appropriate target in *some, not all* temperate forests (the tropics are
>another story).
>
>AND - I would be the last person to condone logging significant old growth
>forests west of the Cascades crest, even though I strongly support the use of
>timber (a renewable resource) over steel and other building materials that, to
>me, pose a greater "threat" to the health of the planet.
>
>
>Ann Camp

I'm interested in your fire history comment can you give me a published
reference to this interpretation?  We have a similar fire history in some
of our eucalypt forests

Thankyou

_____________________________________________________________________
Dr John Banks                                Email: John.Banks@anu.edu.au
Forestry Dept                                tel:    +61 62 249 3632
Australian National University               fax:    +61 62 249 0746
Canberra    2601




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