模拟氮沉降对南亚热带两种乔木幼苗生物量及其分配的影响

doi:10.17521/cjpe.2005.0073

植物生态学报 ›› 2005, Vol. 29 ›› Issue (4): 543-549.DOI: 10.17521/cjpe.2005.0073

模拟氮沉降对南亚热带两种乔木幼苗生物量及其分配的影响

李德军¹^,²^,³, 莫江明¹^,^*(), 方运霆¹, 李志安¹

1 中国科学院华南植物园鼎湖山森林生态系统定位研究站,广东肇庆 526070
2 中国科学院广州地球化学研究所有机地球化学国家重点实验室,广州 510640
3 中国科学院研究生院,北京 100039

收稿日期:2004-01-05 接受日期:2004-12-20 出版日期:2005-01-05 发布日期:2005-07-31
通讯作者: 莫江明
基金资助:
国家自然科学基金项目(30270283);广东省自然科学基金项目(021524);中国科学院知识创新工程领域前沿项目;中国科学院华南植物研究所所长基金项目

EFFECTS OF SIMULATED NITROGEN DEPOSITION ON BIOMASS PRODUCTION AND ALLOCATION IN SCHIMA SUPERBA AND CRYPTOCARYA CONCINNA SEEDLINGS IN SUBTROPICAL CHINA

LI De-Jun¹^,²^,³, MO Jiang-Ming¹^,^*(), FANG Yun-Ting¹, LI Zhi-An¹

1 Dinghushan Forest Ecosystem Research Station, South China Botanical Garden, Chinese Academy of Sciences, Zhaoqing, Guangdong 526070, China
2 State Key Laboratory of Organic Geochemistry, Guangzhou Institute of Geochemistry, Chinese Academy of Sciences, Guangzhou 510640, China
3 Graduate School of Chinese Academy of Sciences, Beijing 100039, China

Received:2004-01-05 Accepted:2004-12-20 Online:2005-01-05 Published:2005-07-31
Contact: MO Jiang-Ming
About author:* E-mail: mojm@scib.ac.cn

摘要/Abstract

摘要：

探讨了南亚热带季风常绿阔叶林两种优势树种荷木(Schima superba)和黄果厚壳桂(Cryptocarya concinna)幼苗的生物量及其分配对氮沉降增加的响应。实验分为对照(CK)、T₅、T₁₀、T₁₅和T₃₀ 5个处理,每个处理设置3次重复。所施氮肥为NH₄NO₃,以溶液方式喷施,5个处理浓度分别为0、0.12、0.24、0.36、0.72 mol N·L^-1。每月喷施2次,5个样方1年喷施的总氮量分别相当于氮沉降率0、5、10、15、30 g N·m^-2·a^-1。经过11个月的施氮处理,两种幼苗对氮沉降的响应存在差异,其中黄果厚壳桂幼苗的基径、株高、全株生物量和相对生长速率除最高处理T₃₀外,均高于对照,但荷木幼苗的基径、全株生物量和相对生长速率除T₁₀外,均小于对照。氮处理也对生物量的分配产生了明显的影响,两种幼苗的叶重比以T₃₀最低,表明高氮处理不利于幼苗叶片的生长;枝重比均以T₃₀最高,反映了高氮处理的幼苗生物量分配到枝干的比例最高;根重比和根冠比均以对照样方幼苗的最高,表明氮处理抑制根的生长,分配到根部分的生物量下降。总的来看,经过11个月的处理,除最高处理T₃₀外,氮处理仍对黄果厚壳桂幼苗的生长有促进作用,而对荷木幼苗的生长则趋向于一定程度的抑制效应,表明黄果厚壳桂幼苗更能耐受高氮条件。

关键词: 南亚热带, 氮沉降, 树苗, 生物量, 分配

Abstract:

To better understand the effects of elevated nitrogen deposition on biomass production and allocation in seedlings of Schima superba and Cryptocarya concinna, the dominant species in subtropical monsoon evergreen broadleaved forests in China, a simulated nitrogen deposition field experiment was conducted. S. superba and C. concinna seedlings were exposed to five nitrogen treatments using NH₄NO₃ solutions of 0, 0.12, 0.24, 0.36 and 0.72 mol N·L^-1. Solutions were applied twice a month from January through November, 2003, equivalent to nitrogen deposition rates of 0, 5, 10, 15 and 30 g N·m^-2·a^-1. Each treatment was divided into three subplots and 40 seedlings of each of the two species were transplanted into each subplot. The two species responded differently to the different rates of nitrogen deposition. The stem base diameter, height, whole-plant biomass and relative growth rate of C. concinna seedlings grown in 5, 10, 15 g N·m^-2·a^-1 treatments were all higher than those in the control plot; however, the stem base diameter, height, whole-plant biomass and relative growth rate of treated S. superba seedlings were lower than those in the control plot with the exception of the 10.0 treatment. The leaf-weight ratio of seedlings of the two species was the lowest in the highest treatment, implying that the high N deposition was harmful to the foliage. The branch-and-stem weight ratio of seedlings of both species was the highest in the highest treatment indicating that the biomass allocated to branches and stems increased under high N deposition. The root-weight ratio and the root to shoot ratio of seedlings in the control plots were the highest, demonstrating that the ratio of biomass allocated to roots decreased under the conditions of elevated nitrogen deposition. Overall, except for the highest N treatment, nitrogen additions enhanced the growth of C. concinna but had the opposite effect on S. superba individuals, indicating that C. concinna seedlings were more resistant to high nitrogen loads.

Key words: Subtropics, Nitrogen deposition, Tree seedlings, Biomass production, Allocation

李德军, 莫江明, 方运霆, 李志安. 模拟氮沉降对南亚热带两种乔木幼苗生物量及其分配的影响. 植物生态学报, 2005, 29(4): 543-549. DOI: 10.17521/cjpe.2005.0073

LI De-Jun, MO Jiang-Ming, FANG Yun-Ting, LI Zhi-An. EFFECTS OF SIMULATED NITROGEN DEPOSITION ON BIOMASS PRODUCTION AND ALLOCATION IN SCHIMA SUPERBA AND CRYPTOCARYA CONCINNA SEEDLINGS IN SUBTROPICAL CHINA. Chinese Journal of Plant Ecology, 2005, 29(4): 543-549. DOI: 10.17521/cjpe.2005.0073

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链接本文: https://www.plant-ecology.com/CN/10.17521/cjpe.2005.0073

https://www.plant-ecology.com/CN/Y2005/V29/I4/543

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参考文献 36

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	全株生物量 WPW(g)	叶重比 LWR (g·g^-1)	枝重比 SBWR (g·g^-1)	根重比 RWR (g·g^-1)	根/冠 R/S
荷木 Schima superba
CK	7.07(0.31)^b	0.30(0.02)^a	0.37(0.01)^c	0.34(0.02)^a	0.53(0.06)^a
T₅	5.01(0.60)^b	0.24(0.04)^ab	0.49(0.05)^ab	0.27(0.01)^b	0.40(0.02)^b
T₁₀	11.85(1.39)^a	0.29(0.03)^a	0.41(0.01)^bc	0.30(0.02)^ab	0.42(0.04)^ab
T₁₅	6.66(1.24)^b	0.31(0.02)^a	0.46(0.03)^ab	0.23(0.01)^b	0.31(0.02)^b
T₃₀	4.25(0.27)^b	0.21(0.01)^b	0.51(0.02)^a	0.28(0.02)^ab	0.41(0.04)^ab
黄果厚壳桂 Cryptocarya concinna
CK	4.59(0.73)^b	0.31(0.04)	0.39(0.02)^ab	0.30(0.03)^a	0.44(0.05)^a
T₅	6.51(1.22)^ab	0.36(0.03)	0.36(0.02)^b	0.28(0.02)^ab	0.38(0.05)^a
T₁₀	6.30(1.05)^b	0.34(0.01)	0.42(0.01)^a	0.24(0.01)^bc	0.32(0.02)^b
T₁₅	9.62(2.04)^a	0.36(0.01)	0.43(0.02)^a	0.21(0.02)^c	0.29(0.02)^b
T₃₀	3.92(1.09)^b	0.30(0.01)	0.44(0.01)^a	0.26(0.02)^abc	0.36(0.02)^ab

	全株生物量 WPW(g)	叶重比 LWR (g·g^-1)	枝重比 SBWR (g·g^-1)	根重比 RWR (g·g^-1)	根/冠 R/S
荷木 Schima superba
CK	7.07(0.31)^b	0.30(0.02)^a	0.37(0.01)^c	0.34(0.02)^a	0.53(0.06)^a
T₅	5.01(0.60)^b	0.24(0.04)^ab	0.49(0.05)^ab	0.27(0.01)^b	0.40(0.02)^b
T₁₀	11.85(1.39)^a	0.29(0.03)^a	0.41(0.01)^bc	0.30(0.02)^ab	0.42(0.04)^ab
T₁₅	6.66(1.24)^b	0.31(0.02)^a	0.46(0.03)^ab	0.23(0.01)^b	0.31(0.02)^b
T₃₀	4.25(0.27)^b	0.21(0.01)^b	0.51(0.02)^a	0.28(0.02)^ab	0.41(0.04)^ab
黄果厚壳桂 Cryptocarya concinna
CK	4.59(0.73)^b	0.31(0.04)	0.39(0.02)^ab	0.30(0.03)^a	0.44(0.05)^a
T₅	6.51(1.22)^ab	0.36(0.03)	0.36(0.02)^b	0.28(0.02)^ab	0.38(0.05)^a
T₁₀	6.30(1.05)^b	0.34(0.01)	0.42(0.01)^a	0.24(0.01)^bc	0.32(0.02)^b
T₁₅	9.62(2.04)^a	0.36(0.01)	0.43(0.02)^a	0.21(0.02)^c	0.29(0.02)^b
T₃₀	3.92(1.09)^b	0.30(0.01)	0.44(0.01)^a	0.26(0.02)^abc	0.36(0.02)^ab

	侧根最大长度 Maximum length of lateral roots (cm)	主根长度 Taproot length (cm)
荷木 Schima superba
CK	13.99(1.25)	6.37(0.34)^b
T₅	10.68(2.28)	6.47(1.33)^b
T₁₀	16.08(5.88)	10.70(3.39)^a
T₁₅	11.00(1.67)	6.03(0.35)^b
T₃₀	11.10(1.89)	7.49(0.04)^ab
黄果厚壳桂 Cryptocarya concinna
CK	21.07(2.26)^a	14.24(1.78)
T₅	17.29(0.62)^ab	13.11(1.60)
T₁₀	14.20(1.89)^bc	12.11(1.89)
T₁₅	12.83(0.48)^bc	12.04(0.79)
T₃₀	10.68(2.83)^c	10.62(2.88)

	侧根最大长度 Maximum length of lateral roots (cm)	主根长度 Taproot length (cm)
荷木 Schima superba
CK	13.99(1.25)	6.37(0.34)^b
T₅	10.68(2.28)	6.47(1.33)^b
T₁₀	16.08(5.88)	10.70(3.39)^a
T₁₅	11.00(1.67)	6.03(0.35)^b
T₃₀	11.10(1.89)	7.49(0.04)^ab
黄果厚壳桂 Cryptocarya concinna
CK	21.07(2.26)^a	14.24(1.78)
T₅	17.29(0.62)^ab	13.11(1.60)
T₁₀	14.20(1.89)^bc	12.11(1.89)
T₁₅	12.83(0.48)^bc	12.04(0.79)
T₃₀	10.68(2.83)^c	10.62(2.88)

模拟氮沉降对南亚热带两种乔木幼苗生物量及其分配的影响

EFFECTS OF SIMULATED NITROGEN DEPOSITION ON BIOMASS PRODUCTION AND ALLOCATION IN SCHIMA SUPERBA AND CRYPTOCARYA CONCINNA SEEDLINGS IN SUBTROPICAL CHINA

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