Kim Mee-Sook, Blaedow Ryan A, McKeever Katie, Olatinwo Rabiu O, Klopfenstein Ned B
USDA Forest Service Pacific Northwest Research Station, 3200 SW Jefferson Way, Corvallis, Oregon, United States, 97331;
USDA Forest Service Region 8, Asheville, North Carolina, United States;
Plant Dis. 2023 Jan 23. doi: 10.1094/PDIS-11-22-2689-PDN.
Armillaria root disease is among the largest causes of mortality and lost productivity of widely ranging horticultural, urban, and forest trees/shrubs in diverse boreal, temperate, and tropical regions around the world (Kim et al. 2022). Damage from Armillaria root disease will likely increase in response to changing climate and extreme weather because environmental stress can predispose host trees to Armillaria root disease (Murray and Leslie 2021; Kim et al. 2021). On August 14, 2021, a mature black oak (Quercus velutina) ca. 29 m in height and 64 cm DBH experienced a complete structural failure originating at the root plate, falling onto a major highway within the Pisgah National Forest near Brevard, North Carolina (35°16'50.876"N, 82°42'51.785"W, elevation 680 m) during sunny, calm conditions. No above-ground indications of predisposing disturbance, injury, or insect/disease activity were observed. Advanced wood decay, however, was present in many structural roots of the exposed root plate; abundant rhizomorphs attached to the surfaces of most roots were noted (Supplemental Figure 1). One large primary root (ca. 23 cm in diameter) exhibited clear signs of Armillaria root disease at the point of failure as evidenced by an extensive decay column, abundant black rhizomorphs on the root surface, and white mycelial fans (a sign of pathogenicity) within the root itself (Supplemental Figure 1). Rhizomorph samples were established in culture, two Armillaria isolates (PNF#001R-1 and PNF#001R-2) were examined, and pairing tests showed that both isolates belonged to the same genet (PNF#001R-1 = PNF#001R-2). Based on translation elongation factor 1α (tef1) sequences, both isolates (one genet) were identified as A. solidipes (GenBank accession no. OP823701), showing 98% similarity with A. solidipes tef1 sequences (e.g., MH879015) in GenBank. Also, nine replications of somatic incompatibility tests of the isolate with five North American Armillaria spp. [A. solidipes, A. mellea, A. gallica, A. mexicana, and Desarmillaria caespitosa (= North American A. tabescens)] showed 67% compatibility with A. solidipes, compared with 0-22% for A. mellea, D. caespitosa, A. gallica, and A. mexicana. All test species but A. mexicana are reported to occur in the eastern and/or southern USA, while A. mexicana occurs in a similar environment in Mexico (Elías-Román et al. 2018). To our knowledge, this is the first confirmed report of A. solidipes in North Carolina, USA, where it was causing disease on black oak, and this is the most southerly confirmed case of A. solidipes in eastern North America. Although Armillaria inoculation tests are impractical, black oak was previously reported as a host of A. solidipes in Massachusetts, USA (Brazee and Wick 2009). Armillaria solidipes is considered as the most important Armillaria root disease pathogen of conifer forests in western USA (Lockman and Kearns 2016), but it has been suggested that A. solidipes can thrive in northern hardwood forests that reside near conifer forests (Brazee and Wick 2009). Climate change is predicted to increase damage caused by A. solidipes on conifers in the western USA (Kim et al. 2021); however, it is undetermined if the occurrence of A. solidipes-caused disease in North Carolina is related to climate change or how climate change could influence this disease across the region. More surveys are needed to assess the impact of Armillaria root disease on health of mixed forests in the eastern USA.
蜜环菌根腐病是导致世界各地不同寒带、温带和热带地区广泛种植的园艺、城市及森林树木/灌木死亡和生产力损失的主要原因之一(Kim等人,2022年)。由于环境压力会使寄主树木易患蜜环菌根腐病,预计气候变化和极端天气将导致蜜环菌根腐病造成的损害增加(Murray和Leslie,2021年;Kim等人,2021年)。2021年8月14日,一棵成熟的黑栎(Quercus velutina),高约29米,胸径64厘米,在根部发生了完全的结构故障,在阳光充足、天气平静的情况下,倒在了北卡罗来纳州布雷瓦德附近皮斯加国家森林内的一条主要公路上(北纬35°16'50.876",西经82°42'51.785",海拔680米)。未观察到地上有易发病的干扰、损伤或昆虫/疾病活动迹象。然而,暴露的根盘的许多结构根中存在严重的木材腐烂;注意到大多数根表面附着有大量菌索(补充图1)。一条大的主根(直径约23厘米)在断裂处表现出蜜环菌根腐病的明显迹象,如广泛的腐烂柱、根表面大量黑色菌索以及根内部的白色菌丝扇(致病性迹象)(补充图1)。将菌索样本进行培养,对两个蜜环菌分离株(PNF#001R - 1和PNF#001R - 2)进行检测,配对试验表明这两个分离株属于同一遗传型(PNF#001R - 1 = PNF#001R - 2)。基于翻译延伸因子1α(tef1)序列,两个分离株(一个遗传型)被鉴定为奥氏蜜环菌(Armillaria solidipes)(GenBank登录号OP823701),与GenBank中奥氏蜜环菌tef1序列(如MH879015)显示出98%的相似性。此外,该分离株与五种北美蜜环菌属物种进行的体细胞不亲和性测试的九次重复试验[奥氏蜜环菌、蜜环菌(Armillaria mellea)、高卢蜜环菌(Armillaria gallica)、墨西哥蜜环菌(Armillaria mexicana)和丛生脱蜜环菌(Desarmillaria caespitosa = 北美亮白蜜环菌(Armillaria tabescens))]显示,与奥氏蜜环菌的相容性为67%,而与蜜环菌、丛生脱蜜环菌、高卢蜜环菌和墨西哥蜜环菌的相容性为0 - 22%。据报道,除墨西哥蜜环菌外,所有测试物种都出现在美国东部和/或南部,而墨西哥蜜环菌出现在墨西哥的类似环境中(Elías - Román等人,2018年)。据我们所知,这是美国北卡罗来纳州首次确认的奥氏蜜环菌病例,它在那里导致黑栎发病,这也是北美东部奥氏蜜环菌最南端的确诊病例。尽管蜜环菌接种试验不切实际,但此前在美国马萨诸塞州黑栎被报道为奥氏蜜环菌的寄主(Brazee和Wick,2009年)。奥氏蜜环菌被认为是美国西部针叶林最重要的蜜环菌根腐病病原菌(Lockman和Kearns,2016年),但有人认为奥氏蜜环菌可以在靠近针叶林的北方硬木林中生长旺盛(Brazee和Wick,2009年)。预计气候变化将增加美国西部奥氏蜜环菌对针叶树造成的损害(Kim等人,2021年);然而,奥氏蜜环菌在北卡罗来纳州引起的疾病发生是否与气候变化有关,以及气候变化如何影响该地区的这种疾病尚不确定。需要更多的调查来评估蜜环菌根腐病对美国东部混交林健康的影响。