The Ecological Importance of California’s Rim Fire

The Eco­log­i­cal Impor­tance of California’s Rim Fire 

- by Chad Han­son, John Muir Project 

Pho­to: Doug Bevington

Since the Rim fire began in the cen­tral Sier­ra Neva­da on August 17, there has been a steady stream of fear­ful, hyper­bol­ic, and mis­in­formed report­ing in much of the media. The fire, which is cur­rent­ly 188,000 acres in size and cov­ers por­tions of the Stanis­laus Nation­al For­est and the north­west­ern cor­ner of Yosemite Nation­al Park, has been con­sis­tent­ly described as “cat­a­stroph­ic”, “destruc­tive”, and “dev­as­tat­ing.” One sto­ry fea­tured a quote from a local man who said he expect­ed “noth­ing to be left”. How­ev­er, if we can, for a moment, set aside the fear, the pan­ic, and the decades of mis­un­der­stand­ing about wild­land fires in our forests, it turns out that the facts dif­fer dra­mat­i­cal­ly from the pop­u­lar mis­con­cep­tions. The Rim fire is a good thing for the health of the for­est ecosys­tem. It is not dev­as­ta­tion, or loss. It is eco­log­i­cal restoration.

What rel­a­tive­ly few peo­ple in the gen­er­al pub­lic under­stand at present is that large, intense fires have always been a nat­ur­al part of fire regimes in Sier­ra Neva­da forests. Patch­es of high-inten­si­ty fire, where­in most or all trees are killed, cre­ates “snag for­est habi­tat,” which is the rarest, and one of the most eco­log­i­cal­ly impor­tant, for­est habi­tat types in the entire Sier­ra Neva­da. Con­trary to com­mon myths, even when for­est fires burn hottest, only a tiny pro­por­tion of the above­ground bio­mass is actu­al­ly con­sumed (typ­i­cal­ly less than 3 per­cent). Habi­tat is not lost. Far from it. Instead, mature for­est is trans­formed into “snag for­est”, which is abun­dant in stand­ing fire-killed trees, or “snags,” patch­es of native fire-fol­low­ing shrubs, downed logs, col­or­ful flow­ers, and dense pock­ets of nat­ur­al conifer regeneration. 

This for­est reju­ve­na­tion begins in the first spring after the fire. Native wood-bor­ing bee­tles rapid­ly col­o­nize burn areas, detect­ing the fires from dozens of miles away through infrared recep­tors that these species have evolved over mil­len­nia, in a long rela­tion­ship with fire. The bee­tles bore under the bark of stand­ing snags and lay their eggs, and the lar­vae feed and devel­op there. Wood­peck­er species, such as the rare and imper­iled black-backed wood­peck­er (cur­rent­ly pro­posed for list­ing under the Endan­gered Species Act), depend upon snag for­est habi­tat and wood-bor­ing bee­tles for survival.

One black-backed wood­peck­er eats about 13,500 bee­tle lar­vae every year — and that gen­er­al­ly requires at least 100 to 200 stand­ing dead trees per acre. Black-backed wood­peck­ers, which are nat­u­ral­ly cam­ou­flaged against the charred bark of a fire-killed tree, are a key­stone species, and they exca­vate a new nest cav­i­ty every year, even when they stay in the same ter­ri­to­ry. This cre­ates homes for numer­ous sec­ondary cav­i­ty-nest­ing species, like the moun­tain blue­bird (and, occa­sion­al­ly, squir­rels and even martens), that can­not exca­vate their own nest cav­i­ties. The native flow­er­ing shrubs that ger­mi­nate after fire attract many species of fly­ing insects, which pro­vide food for fly­catch­ers and bats; and the shrubs, new conifer growth, and downed logs pro­vide excel­lent habi­tat for small mam­mals. This, in turn, attracts rap­tors, like the Cal­i­for­nia spot­ted owl and north­ern goshawk, which nest and roost main­ly in the low/­mod­er­ate-inten­si­ty fire areas, or in adja­cent unburned for­est, but active­ly for­age in the snag for­est habi­tat patch­es cre­at­ed by high-inten­si­ty fire — a sort of “bed­room and kitchen” effect. Deer thrive on the new growth, black bears for­age hap­pi­ly on the rich source of berries, grubs, and small mam­mals in snag for­est habi­tat, and even rare car­ni­vores like the Pacif­ic fish­er active­ly hunt for small mam­mals in this post-fire habitat.

In fact, every sci­en­tif­ic study that has been con­duct­ed in large, intense fires in the Sier­ra Neva­da has found that the big patch­es of snag for­est habi­tat sup­port lev­els of native bio­di­ver­si­ty and total wildlife abun­dance that are equal to or (in most cas­es) high­er than old-growth for­est. This has been found in the Don­ner fire of 1960, the Man­ter and Stor­rie fires of 2000, the McNal­ly fire of 2002, and the Moon­light fire of 2007, to name a few. Wildlife abun­dance in snag for­est increas­es up to about 25 or 30 years after fire, and then declines as snag for­est is replaced by a new stand of for­est (increas­ing again, sev­er­al decades lat­er, after the new stand becomes old for­est). The wood­peck­ers, like the black-backed wood­peck­er, thrive for 7 to 10 years after fire gen­er­al­ly, and then must move on to find a new fire, as their bee­tle lar­vae prey begins to dwin­dle. Fly­catch­ers and oth­er birds increase after 10 years post-fire, and con­tin­ue to increase for anoth­er two decades. Thus, snag for­est habi­tat is ephemer­al, and native bio­di­ver­si­ty in the Sier­ra Neva­da depends upon a con­stant­ly replen­ished sup­ply of new fires. 

It would sur­prise most peo­ple to learn that snag for­est habi­tat is far rar­er in the Sier­ra Neva­da than old-growth for­est. There are about 1.2 mil­lion acres of old-growth for­est in the Sier­ra, but less than 400,000 acres of snag for­est habi­tat, even after includ­ing the Rim fire to date. This is due to fire sup­pres­sion, which has, over decades, sub­stan­tial­ly reduced the aver­age annu­al amount of high-inten­si­ty fire rel­a­tive to his­toric lev­els, accord­ing to mul­ti­ple stud­ies. Because of this, and the com­bined impact of exten­sive post-fire com­mer­cial log­ging on nation­al for­est lands and pri­vate lands, we have far less snag for­est habi­tat now than we had in the ear­ly twen­ti­eth cen­tu­ry, and before. This has put numer­ous wildlife species at risk. These are species that have evolved to depend upon the many habi­tat fea­tures in snag for­est — habi­tat that can­not be cre­at­ed by any oth­er means. Fur­ther, high-inten­si­ty fire is not increas­ing cur­rent­ly, accord­ing to most stud­ies (and con­trary to wide­spread assump­tions), and our forests are get­ting wet­ter, not dri­er (accord­ing to every study that has empir­i­cal­ly inves­ti­gat­ed this ques­tion), so we can­not afford to be cav­a­lier and assume that there will be more fire in the future, despite fire sup­pres­sion efforts.  We will need to pur­pose­ful­ly allow more fires to burn, espe­cial­ly in the more remote forests.

The black-backed wood­peck­er, for exam­ple, has been reduced to a mere sev­er­al hun­dred pairs in the Sier­ra Neva­da due to fire sup­pres­sion, post-fire log­ging, and com­mer­cial thin­ning of forests, cre­at­ing a sig­nif­i­cant risk of future extinc­tion unless for­est man­age­ment poli­cies change, and unless for­est plans on our nation­al forests include pro­tec­tions (which they cur­rent­ly do not). This species is a “man­age­ment indi­ca­tor species”, or bell­wether, for the entire group of species asso­ci­at­ed with snag for­est habi­tat. As the black-backed wood­peck­er goes, so too do many oth­er species, includ­ing some that we prob­a­bly don’t yet know are in trou­ble. The Rim fire has cre­at­ed valu­able snag for­est habi­tat in the area in which it was need­ed most in the Sier­ra Neva­da: the west­ern slope of the cen­tral por­tion of the range. Even the For­est Service’s own sci­en­tists have acknowl­edged that the lev­els of high-inten­si­ty fire in this area are unnat­u­ral­ly low, and need to be increased. In fact, the last mod­er­ate­ly sig­nif­i­cant fires in this area occurred about a decade ago, and there was a sub­stan­tial risk that a 200-mile gap in black-backed wood­peck­ers pop­u­la­tions was about to devel­op, which is not a good sign from a con­ser­va­tion biol­o­gy stand­point. The Rim fire has helped this sit­u­a­tion, but we still have far too lit­tle snag for­est habi­tat in the Sier­ra Neva­da, and no pro­tec­tions from the eco­log­i­cal dev­as­ta­tion of post-fire logging.

Recent sci­en­tif­ic stud­ies have caused sci­en­tists to sub­stan­tial­ly revise pre­vi­ous assump­tions about his­toric fire regimes and for­est struc­ture. We now know that Sier­ra Neva­da forests, includ­ing pon­derosa pine and mixed-conifer forests, were not homoge­nous­ly “open and park­like” with only low-inten­si­ty fire. Instead, many lines of evi­dence, and many pub­lished stud­ies, show that these areas were often very dense, and were dom­i­nat­ed by mixed-inten­si­ty fire, with high-inten­si­ty fire pro­por­tions rang­ing gen­er­al­ly from 15 per­cent to more than 50 per­cent, depend­ing upon the fire and area. Numer­ous his­toric sources, and recon­struc­tions, doc­u­ment that large high-inten­si­ty fire patch­es did in fact occur pri­or to fire sup­pres­sion and log­ging. Often these patch­es were hun­dreds of acres in size, and occa­sion­al­ly they were thou­sands — even tens of thou­sands — of acres. So, there is no eco­log­i­cal rea­son to fear or lament fires like the Rim fire, espe­cial­ly in an era of ongo­ing fire deficit. 

Most fires, of course, are much small­er, and less intense than the Rim fire, includ­ing the oth­er fires occur­ring this year. Over the past quar­ter-cen­tu­ry fires in the Sier­ra Neva­da have been dom­i­nat­ed on aver­age by low/­mod­er­ate-inten­si­ty effects, includ­ing in the areas that have not burned in sev­er­al decades. But, after decades of fear-induc­ing, tax­pay­er-sub­si­dized, anti-fire pro­pa­gan­da from the US For­est Ser­vice, it is rel­a­tive­ly eas­i­er for many to accept small­er, less intense fires, and more chal­leng­ing to appre­ci­ate big fires like the Rim fire. How­ev­er, if we are to man­age forests for eco­log­i­cal integri­ty, and main­tain the full range of native wildlife species on the land­scape, it is a chal­lenge that we must embrace. 

Encour­ag­ing­ly, the pre­vi­ous assump­tion about a ten­sion between the restora­tion of more fire in our forests and home pro­tec­tion has proven to be false. Every study that has inves­ti­gat­ed this issue has found that the only way to effec­tive­ly pro­tect homes is to reduce com­bustible brush in “defen­si­ble space” with­in 100 to 200 feet of indi­vid­ual homes. Cur­rent for­est man­age­ment pol­i­cy on nation­al for­est lands, unfor­tu­nate­ly, remains heav­i­ly focused not only on sup­press­ing fires in remote wild­lands far from homes, but also on inten­sive mechan­i­cal “thin­ning” projects — which typ­i­cal­ly involve the com­mer­cial removal of upwards of 80 per­cent of the trees, includ­ing mature trees and often old-growth trees —that are most­ly a long dis­tance from homes. This not only diverts scarce resources away from home pro­tec­tion, but also gives home­own­ers a false sense of secu­ri­ty because a fed­er­al agency has implied, incor­rect­ly, that they are now pro­tect­ed from fire — a con­text that puts homes fur­ther at risk. 

The new sci­en­tif­ic data is telling us that we need not fear fire in our forests. Fire is doing impor­tant and ben­e­fi­cial eco­log­i­cal work, and we need more of it, includ­ing the occa­sion­al large, intense fires. Nor do we need to bal­ance home pro­tec­tion with the restora­tion of fire’s role in our forests. The two are not in con­flict. We do, how­ev­er, need to muster the courage to tran­scend our fears and out­dat­ed assump­tions about fire. Our for­est ecosys­tems will be bet­ter for it. 

Chad Han­son, the direc­tor of the John Muir Project (JMP) of Earth Island Insti­tute, has a Ph.D. in ecol­o­gy from the Uni­ver­si­ty of Cal­i­for­nia at Davis, and focus­es his research on for­est and fire ecol­o­gy in the Sier­ra Neva­da. He can be reached at cthanson1@gmail.com, or vis­it JMP’s web­site at www.johnmuirproject.org for more infor­ma­tion, and for cita­tions to spe­cif­ic stud­ies per­tain­ing to the points made in this article.


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