热带亚热带植物学报
熱帶亞熱帶植物學報
열대아열대식물학보
JOURNAL OF TROPICAL AND SUBTROPICAL BOTANY
2014年
5期
479-485
,共7页
刘佳庆%李宁%熊天石%邓青珊%时光黎%鲁长虎
劉佳慶%李寧%熊天石%鄧青珊%時光黎%魯長虎
류가경%리저%웅천석%산청산%시광려%로장호
南方红豆杉%种群结构%天然更新%濒危植物
南方紅豆杉%種群結構%天然更新%瀕危植物
남방홍두삼%충군결구%천연경신%빈위식물
Taxus chinensis var. mairei%Population structure%Nature regeneration%Endangered plant
为了解南方红豆杉(Taxus chinensis var. mairei)不同种群的结构变化,于2007年、2008年、2012年分别对皖南仙寓山双坑村、浙江天目山桐坑村及福建梅花山的南方红豆杉天然种群进行了研究。结果表明,仙寓山的1214株南方红豆杉中,幼苗占80%;天目山有510株,幼苗占39.61%,其次是9 m以上的古树,占22.16%;梅花山有174株,幼苗占70.11%,古树占20.11%。3个种群的天然更新都呈缓慢增长状态,存活曲线为Deevey-Ⅲ型,空间分布均为聚集分布,但从幼苗到幼树的生长阶段死亡率高。因此,对濒危植物南方红豆杉的保护重点应放在幼苗和幼树阶段。
為瞭解南方紅豆杉(Taxus chinensis var. mairei)不同種群的結構變化,于2007年、2008年、2012年分彆對皖南仙寓山雙坑村、浙江天目山桐坑村及福建梅花山的南方紅豆杉天然種群進行瞭研究。結果錶明,仙寓山的1214株南方紅豆杉中,幼苗佔80%;天目山有510株,幼苗佔39.61%,其次是9 m以上的古樹,佔22.16%;梅花山有174株,幼苗佔70.11%,古樹佔20.11%。3箇種群的天然更新都呈緩慢增長狀態,存活麯線為Deevey-Ⅲ型,空間分佈均為聚集分佈,但從幼苗到幼樹的生長階段死亡率高。因此,對瀕危植物南方紅豆杉的保護重點應放在幼苗和幼樹階段。
위료해남방홍두삼(Taxus chinensis var. mairei)불동충군적결구변화,우2007년、2008년、2012년분별대환남선우산쌍갱촌、절강천목산동갱촌급복건매화산적남방홍두삼천연충군진행료연구。결과표명,선우산적1214주남방홍두삼중,유묘점80%;천목산유510주,유묘점39.61%,기차시9 m이상적고수,점22.16%;매화산유174주,유묘점70.11%,고수점20.11%。3개충군적천연경신도정완만증장상태,존활곡선위Deevey-Ⅲ형,공간분포균위취집분포,단종유묘도유수적생장계단사망솔고。인차,대빈위식물남방홍두삼적보호중점응방재유묘화유수계단。
In order to understand the structure changes of different Chinese yew (Taxus chinensis var. mairei) populations, the regeneration populations of Chinese yew, distributing in Shuangkeng Village in Xianyu Mountain of Anhui Province, Tongkeng Village in Tianmu Mountain of Zhejiang Province and Ecological Garden of Yew, Fujian Meihua Mountain National Nature Reserve, respectively, were studied from October to December in 2007, 2008 and 2012. The results showed that there were 1214 individuals Chinese yew in Xianyu Mountain in 2007, the number of seedlings accounting for 80%. Chinese yew distributed in Tianmu Mountain and Meihua Mountain had 510 and 174 individuals, the number of seedlings accounting for 39.61%and 70.11%, the number of tree height more than 9 m for 22.16%and 20.11%, respectively. All of the three natural regeneration populations showed slowly increasing and the survival curves were Deevey-Ⅲtype with clumped spatial pattern, and the mortality at growth stage from seedlings to saplings was high. It was suggested that the protect priority to rare and endangered T. chinensis var. mairei should be placed in stages from seedlings and saplings.