|Table of Contents|

Effect of Heavy Metal Stress on Germination,Growth and Photosynthetic Characteristics of Poa pratensis L.(PDF)

《北方园艺》[ISSN:1001-0009/CN:23-1247/S]

Issue:
2016年18
Page:
61-64
Research Field:
Publishing date:

Info

Title:
Effect of Heavy Metal Stress on Germination,Growth and Photosynthetic Characteristics of Poa pratensis L.
Author(s):
YIN Juan1LI Ning2
(1.Forestry Institute,Xinyang Agroforestry Institute,Xinyang,Henan 464000;2.Department of Environmental Art Engineering,Henan Vocational and Technical College,Zhengzhou,Henan 450046)
Keywords:
Poa pratensis L.heavy metalgerminationgrowthphotosynthetic characteristics
PACS:
-
DOI:
10.11937/bfyy.201618017
Abstract:
In the experiment,Poa pratensis L.was selected as the research material,the effect of three different heavy metals ions cadmium(Cd2+),copper(Cu2+),lead(Pb2+) and different concentration on seed germination,seedling growth and photosynthetic characteristic systematically were studied.The results showed that in the low concentration of Cd2+ (10 mg?kg-1) and Cu2+ (100 mg?kg-1) treatments,seed germination of Poa pratensis L.had been promoted in some extent and the seed germination rates reached 962% and 942% respectively,the germination index were 98 and 97 respectively,which were higher than the controls.When the concentration of Cd2+ was higher than 10 mg?kg-1 or Cu2+ concentration was higher than 100 mg?kg-1,the seed germination percentage and germination index were lower than the controls.When Cu2+ concentration was below 200 mg?kg-1,the seedlings height,total root length,biomass of aboveground and the content of chlorophyll,Fv/Fm values had a slight increase along with the increase of concentration.When Cu2+ concentration was higher than 200 mg?kg-1,significant decline appeared with the increase of concentration.In addition,seed germination,seedling growth and photosynthetic efficiency of Poa pratensis L.declined with the increase of concentration of Pb2+,and were lower than the controls.

References:

 

[1]陈俊任,柳丹,吴家森,.重金属胁迫对毛竹种子萌发及其富集效应的影响[J].生态学报,2014(22):6501-6509.

[2]田禹璐,朱宏.重金属镉对植物胁迫的研究进展[J].哈尔滨师范大学自然科学学报,2015(2):149-153.

[3]梁剑.重金属镉胁迫对油橄榄幼苗生长的影响[J].江苏农业科学,2015(11):110-112.

[4]李西,吴亚娇,孙凌霞.铅胁迫对三种暖季型草坪草生长和生理特性的影响[J].草业学报,2014(4):171-180.

[5]杨玲,张勇,吴洪娇,.铅锌胁迫对早熟禾和狗牙根种子出苗和幼苗生长的影响[J].云南农业大学学报(自然科学版),2013,28(3):405-410.

[6]王松华,张华,何庆元.铜胁迫对紫花苜蓿幼苗叶片抗氧化系统的影响[J].应用生态学报,2011(9):2285-2290.

[7]尹莹莹.干旱胁迫下草地早熟禾叶片的生长模型[J].贵州农业科学,2015(12):45-47.

[8]梁芳,郭晋平.植物重金属毒害作用机理研究进展[J].山西农业科学,2007(11):34-36.

[9]马敏,龚惠红,邓泓.重金属对8种园林植物种子萌发及幼苗生长的影响[J].中国农学通报,2012,28(22):206-211.

[10]陈伟.重金属胁迫对草坪草生长发育及生理特性的影响[D].兰州:甘肃农业大学,2014.

[11]沈高峰.重金属Pb胁迫对草坪草生长·抗氧化生理特性的影响[J].安徽农业科学,201139(24):14757-14760.

[12]多立安,高玉葆,赵树兰.早熟禾对4种重金属胁迫生长响应特征[J].西北植物学报,2006,26(1):183-187.

[13]刘大林,杨俊俏,刘兆明,.镉、铅胁迫对草地早熟禾幼苗生理的影响[J].草业科学,2015,32(2):224-230.

Memo

Memo:
-
Last Update: 2016-10-31