The California Chaparral Institute

...the voice of the chaparral

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CHAPARRAL MYTHS

Chaparral Mythology

Chaparral is misunderstood primarily because most people do not recognize it. What happens in forests is frequently misapplied to chaparral. Since most of Southern California National Forests are dominated by chaparral, not timber (Cleveland National Forest is 88% chaparral), it's important Southern Californians be aware of the misconceptions about the state's dominant plant community. Proper understanding is especially crucial now because there is a vocal minority promoting poor land management practices motivated by economic self interest. These folks claim the the so-called "wildfire crisis" in California can only be solved by grinding or burning backcountry chaparral to reduce the amount of vegetation available to burn.

Myth #1: Chaparral needs fire to "renew" and clean out "built-up" brush.

As an ecosystem, chaparral does not "need" fire to remain healthy. Old-growth chaparral continues to be productive, growing fresh, new growth in its upper canopy every year. In fact, some chaparral plants require the leaf litter and shade provided by older chaparral stands for their seeds to germinate successfully. Instead of becoming "trashy" or unproductive, as some have claimed, thirty-year-old chaparral is actually just beginning a new cycle of life. To find out what old-growth chaparral is really like and to download a recent paper discussing how old-growth chaparral recovers from wildfire, please go to our Old-Growth page.

Myth #2: Past fire suppression has built up "unnatural" levels of fuel (vegetation) in the chaparral.

The California Statewide Fire History Database clearly shows acreage burned per decade over the past 100 years in southern California has remained relatively constant, despite truly heroic attempts by firefighters. Unlike some forests, fire has NOT been excluded from the chaparral. In fact, fire frequency in southern California has been increasing dramatically over the past century.

The natural fire return interval for chaparral was probably anywhere from 30 to 200+ years. No one really knows. Careful, objective statistical analyses by scientists at UC Berkeley and the US Geological Survey has found no significant change in the probability of chaparral burning as it ages except a slight reduction in risk in stands less than about 5 years old. Slight tendencies don’t provide much solace in the face of our inevitable Santa Ana firestorms, which sweep through all vegetation age classes. The notion that a mosaic (patches of different aged chaparral) will prevent large firestorms is not supported by data collected over the past ten years.

Testing a Basic Assumption of Shrubland Fire Management: how important is fuel age? M.A. Moritz, J.E. Keeley, E.A. Johnson, A.A. Schaffner (2004).

Reexamining Fire Suppression Impacts on Brushland Fire Regimes. Keeley, J.E., C.J. Fotheringham, M. Morais (1999).

Southern California Fires Per Decade
Each bar represents the area burned per decade (1900 to 1990) with a 10-year running annual average line during the 20th century for nine California counties. Top row: Monterey, San Luis Obispo, Santa Barbara. Middle row: Ventura, Los Angeles, San Bernardino. Bottom row: Riverside, Orange, San Diego. Horizontal axis in years, vertical axis area burned in hectares. 1 hectares equals 2.47 acres. Adapted from Keeley and Fotheringham 2003 as found in Fire, Chaparral, and Survival in Southern California (Halsey 2005).
 

Myth #3: Large chaparral wildfires are unusual and preventable.

Large chaparral fires have occurred prior to 2003 and will continue to occur.  Southern California has one of the worst fire-prone climates on earth. For example, more than 300,000 acres burned in the Santiago fire during the last week of September, 1889 in Orange County (the 2003 Cedar fire burned 273,246 acres). During the same time period another fire in San Diego County burned more than 60,000 acres. As with modern fire storms, there were numerous other wildfires across Southern California that week. However, the fires didn't inflict much damage on the human community because few people lived in the backcountry back then. Now, with so many homes up against the wilderness, fires can become catastrophic.

"Santa Ana. Sept. 25. - The fire which has been burning for the past two days still continues in the canyons. The burned and burning district now extends over one hundred miles from north to south, and is 10 to 18 miles in width. Over $100,000 worth of pasturage and timber has been destroyed."   Los Angeles Times, September 27, 1889.

The best ways to prevent loss of life and property are to retrofit exisiting structures to make them more fire safe, plan communities so they are not built in high fire risk areas, and maintain proper vegetation management directly around structures.

To examine the latest research on how to prepare for wildfire from the community outward instead of from the wildland inward, see the Fire Information Engine at the Center for Fire Research and Outreach at: http://firecenter.berkeley.edu/fie/. Click on "To see a sample..." to see the process work.

Myth #4: Chaparral is adapted to fire:

It is best to think of each type of chaparral as adapted to a particular fire regime rather than just "fire." This is an important distinction because when people say chaparral is adapted to or needs fire there is no reference to all the important variables involved such as fire frequency, season of burn, intensity (level of heat), or severity (amount of living material consumed). Too much fire (increased frequency) will destroy a chaparral system. Fire during the cool, moist season can seriously damage the seed bank. See our Fire & Nature, Threats and Fire & Science pages for more details.

Myth #5: Chemical inhibition in the chaparral (allelopathy):

Chemical inhibition, or allelopathy, suggests plants are capable of suppressing the growth or germination of neighboring competitors.  Although an intriguing idea, actual chemical inhibition in nature has been notoriously difficult to prove.  “To my knowledge,” wrote plant ecologist J. H. Connell in 1990, “no published field study has demonstrated direct interference by allelopathy in soil…while excluding the possibility of other indirect interactions with resources, natural enemies, or other competitors.”

This lack of scientific verification, however, has not prevented the concept from being presented as a well-understood phenomenon in science texts as well as along chaparral nature trails.  Dramatic explanations are seductive, especially if they provide interesting answers to intriguing problems.  If repeated often enough, they become dogma and influence thinking for decades.

C.H. Muller, an accomplished botanist from the University of California, Santa Barbara, suggested allelopathy explained the lack of plant growth under the canopy of mature chaparral stands in southern California (Muller, et.al. 1968).  According to his hypothesis, chemicals washed off the leaves of chamise and manzanita shrubs, suppressing the germination of seeds in the ground below.  When the chaparral burned, flames denatured the toxic substances releasing the seeds from inhibition.  This resulted in the remarkable number of shrub seedlings and wildflowers emerging in post-fire environments.  The problem with this explanation is that the soil chemicals suspected of suppressing growth actually increase after a fire.  In addition, the dormancy found in chaparral plant seeds is innate, not caused by some outside, environmental factor.  The seeds are dormant before they hit the ground.  Chaparral seed dormancy evolved because poor growing conditions under mature shrubs selected for seed traits postponing germination until those conditions improved.  Under xeric conditions, germinating under a shady canopy with hungry herbivores scurrying around is not a recipe for success.  Fire quickly removes those problems and sets the stage for chaparral renewal.  Post-fire seedling response in chaparral can be easily explained without invoking the notion of chemical inhibition.

Muller also suggested allelopathy was the cause for bare zones often found around purple sage (Salvia leucophylla) and California sagebrush (Artemisia californica) (Muller, et.al. 1964) in the coastal sage scrub community.  Later investigations revealed these bare zones are primarily the work of herbivores (Bartholomew 1971), not volatile substances from the plants themselves.  To little furry rodents like the California mouse (Peromyscus californicus) and the pacific kangaroo rat (Dipodomys agilis) the world is a dangerous place.  Cover is critical to their survival since they are on the dietary preference list of local carnivores like coyotes, snakes, and hawks.  Consequently, they have a tendency to remain under shrubbery with only occasional, quick forays into surrounding grassland to nibble on available seeds or new growth.  They will stray only as far as they can quickly leap back to safety.  Bare zones, therefore, can be viewed as “calculated-risk terrain” where rodents have a fair chance of grabbing food without getting caught.  Bare zones are bare because herbivores exploit the space to grab available snacks.

Do volatile compounds in certain coastal sage scrub plants ever play a role significant enough to make a difference in naturally occurring vegetation patterns?  “As far as I know, the question of why grasses grow within bare zones during wet years, despite animal activity, has never been adequately addressed,” Bob Muller said when reflecting upon his father’s work.  “Why don’t animals always eliminate seedlings, regardless of the level of moisture?

The explanation favored by C.H. Muller provides a reasonable hypothesis for this phenomenon; heavy rains leach toxins from the soil, removing inhibitory chemicals and permitting seedling success.  However, without further investigation the question remains unresolved.

“The critical issue,” John Harper (1975), a prominent plant population biologist from England explained, “is to determine whether such toxicity plays a role in the interactions between plants in the field.  Demonstrating this has proved extraordinarily difficult – it is logically impossible to prove that it doesn’t happen and perhaps nearly impossible to prove absolutely that it does.”

-From "Fire, Chaparral, and Survival in Southern California." See the "Book Excerpts" page for more details.

The full paper dealing with allelopathy has been published in the Journal of the Torrey Botanical Society 131(4), 2004, pp. 343-367, "In search of allelopathy: an eco-historical view of the investigation of chemical inhibition in California coastal sage scrub and chamise chaparral." You may purchase a copy of the actual reprint on our Membership Page. If you are interested in obtaining an electronic copy, please request one by writing us an EMAIL.

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