Crown fires remove a fire-sensitive canopy dominant from oak-juniper woodlands: results from long-term monitoring of wildfires

IF 3.6 3区 环境科学与生态学 Q1 ECOLOGY Fire Ecology Pub Date : 2024-08-22 DOI:10.1186/s42408-024-00311-w
Charlotte M. Reemts, Carla Picinich, Jinelle H. Sperry
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Abstract

In central Texas, re-sprouting oaks (Quercus spp.) co-occur with non-resprouting Ashe juniper (Juniperus ashei) in a mosaic of fire-dependent (oak savanna) and fire-sensitive (oak-juniper woodland) habitats. The region’s mature woodlands are the only nesting habitat for the endangered golden-cheeked warbler (Setophaga chrysoparia). We studied long-term recovery of woodland structure and species composition after single and repeated crown fires on three soil types (mesa, slope, and deep savanna soils). On once-burned sites, density and basal area of non-juniper trees (all woody species except juniper) reached or exceeded unburned levels after 14–24 years, indicating successful recruitment (24 years vs unburned, mesa: 481 ± 254 vs 155 ± 137 stems ha−1, 2 ± 1 vs 1 ± 2 m2 ha−1; slope: 910 ± 330 vs 251 ± 103 stems ha−1, 5 ± 2 vs 3 ± 2 m2 ha−1). Ashe juniper, however, remained mostly absent from burned woodlands (juniper tree density, 24 years vs unburned, mesa: 6 ± 10 vs 691 ± 410 stems ha−1; slope: 20 ± 17 vs 731 ± 183 stems ha−1) and total basal area was 47–87% lower than in unburned areas. In formerly fire-suppressed savannas, non-juniper tree density exceeded unburned levels and juniper density recovered the most (24 years vs unburned, non-juniper: 679 ± 250 vs 251 ± 103 stems ha−1; juniper: deep: 50 ± 71 vs 317 ± 297 stems ha−1). Juniper trees were still absent from twice-burned sites in year 11 and understory density was recovering more slowly, at least on slopes (one fire: 224 ± 206 stems ha−1; two fires: 26 ± 47 stems ha−1). Juniper recovery was correlated with distance to the wildfire perimeter, suggesting that regeneration is limited in part by dispersal. We found successful recruitment of resprouting hardwood species after one and two crown fires, likely due to the low deer densities at Fort Cavazos. In fire-suppressed oak savannas, a single crown fire did not restore savanna structure and Ashe juniper is slowly re-establishing. Long-term restoration of a savanna on these soils will require additional treatments, like repeated prescribed fire. In oak-juniper woodlands, crown fires removed the fire-sensitive Ashe juniper from canopy co-dominance for decades, making the woodlands unsuitable as habitat for golden-cheeked warblers. Given the long-term consequences of crown fires for golden-cheeked warbler habitat, existing mature oak-juniper woodlands should be protected from crown fire.
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冠火清除了橡树-桧木林地中对火敏感的冠层优势:对野火的长期监测结果
在得克萨斯州中部,重新萌发的橡树(栎树属)与未萌发的杜松(杜松属)共同分布在依赖火源的(橡树稀树草原)和对火源敏感的(橡树-杜松林地)栖息地中。该地区的成熟林地是濒临灭绝的金颊莺(Setophaga chrysoparia)唯一的筑巢栖息地。我们研究了三种土壤类型(台地土、斜坡土和深层热带稀树草原土)的林地结构和物种组成在单次和多次树冠火灾后的长期恢复情况。在曾经燃烧过的地点,非桧木树木(除桧木外的所有木本物种)的密度和基部面积在 14-24 年后达到或超过了未燃烧时的水平,这表明成功地进行了更新(24 年与未燃烧时相比,mesa:481 ± 254 vs 155 ± 137 stems ha-1,2 ± 1 vs 1 ± 2 m2 ha-1;斜坡:910 ± 330 vs 251 ± 103 stems ha-1,5 ± 2 vs 3 ± 2 m2 ha-1)。然而,被烧毁的林地中大部分仍然没有杜松(杜松树密度,24 年与未烧毁相比,山丘:6 ± 10 与 691 ± 410 株/公顷-1;山坡:20 ± 17 与 731 ± 183 株/公顷-1),总基部面积比未烧毁地区低 47-87%。在以前受火灾影响的稀树草原上,非杜松树木的密度超过了未焚烧的水平,而杜松的密度恢复最大(24 年与未焚烧相比,非杜松:679 ± 250 株/公顷 vs 251 ± 103 株/公顷;杜松:深:50 ± 71 株/公顷 vs 317 ± 297 株/公顷)。在第 11 年,两次烧毁的地点仍然没有杜松,林下密度的恢复速度较慢,至少在斜坡上是如此(一次火灾:224 ± 206 株/公顷-1;两次火灾:26 ± 47 株/公顷-1)。杜松的恢复与野火周边的距离相关,这表明再生在一定程度上受到扩散的限制。我们发现,在一次和两次树冠大火后,重新萌发的硬木树种都能成功繁殖,这可能是因为卡瓦佐斯堡的鹿密度较低。在受火灾影响的橡树稀树草原上,一次树冠火灾并不能恢复稀树草原的结构,Ashe 杜松正在缓慢地重建。要在这些土壤上长期恢复热带稀树草原,还需要额外的处理方法,如反复使用规定火种。在橡树-桧木林地中,树冠大火使对火敏感的 Ashe juniper 几十年来失去了树冠共生优势,使林地不适合作为金颊莺的栖息地。鉴于冠火对金颊莺栖息地的长期影响,现有的成熟橡树-桧木林地应受到保护,避免冠火。
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来源期刊
Fire Ecology
Fire Ecology ECOLOGY-FORESTRY
CiteScore
6.20
自引率
7.80%
发文量
24
审稿时长
20 weeks
期刊介绍: Fire Ecology is the international scientific journal supported by the Association for Fire Ecology. Fire Ecology publishes peer-reviewed articles on all ecological and management aspects relating to wildland fire. We welcome submissions on topics that include a broad range of research on the ecological relationships of fire to its environment, including, but not limited to: Ecology (physical and biological fire effects, fire regimes, etc.) Social science (geography, sociology, anthropology, etc.) Fuel Fire science and modeling Planning and risk management Law and policy Fire management Inter- or cross-disciplinary fire-related topics Technology transfer products.
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