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铁尾矿修复植物选择研究
引用本文:李想,车晓雨,王锦,张宝娟,李玉灵. 铁尾矿修复植物选择研究[J]. 河北林果研究, 2016, 0(3): 225-229. DOI: 10.13320/j.cnki.hjfor.2016.0044
作者姓名:李想  车晓雨  王锦  张宝娟  李玉灵
作者单位:1. 河北农业大学林学院,河北保定,071000;2. 河北农业大学园林与旅游学院,河北保定,071000;3. 河北农业大学人文社会科学学院,河北保定,071000;4. 天津天狮学院,天津,301700;5. 河北农业大学林学院,河北保定071000; 河北省林木种质资源与森林保护重点实验室,河北保定071000
基金项目:国家林业局林业行业公益专项“环京津生态脆弱区生态经济植被建设技术研究”(201404214);河北省科技支撑计划专题“基于植被恢复的铁尾矿废弃地基质修复技术研究”(12236726D-X )。
摘    要:针对铁尾矿植被恢复时植物可选种类少、适应性差,影响植被修复技术推广的现状,在唐山首钢马兰庄镇铁尾矿废弃地上直接播种紫苜蓿、紫穗槐、皂荚、暴马丁香、刺槐5种植物,对每种植物的株高、地径、根长、地上生物量、地下生物量和根冠比等生长指标进行测定分析,结果表明:到2014年9月,刺槐在5种植物中表现最佳,适应性最强,株高(77.67cm)、地径(6.33cm)、根长(23.97cm)、地上生物量(2 040.19g/m~2)和地下生物量(839.01g/m~2)及这5种指标的年生长量均达最大值;除地径外,紫苜蓿的各项生长指标表现次之;紫穗槐、暴马丁香、皂荚较差。2013年9月,各植物的根冠比由大到小依次为紫穗槐(1.04)、皂荚(0.83)、暴马丁香(0.56)、刺槐(0.37)、紫苜蓿(0.32);2014年9月各植物的根冠比由大到小依次为皂荚(1.71)、暴马丁香(0.91)、紫穗槐(0.80)、紫苜蓿(0.50)、刺槐(0.41)。综合考虑,刺槐和紫苜蓿可分别作为适宜铁尾矿修复的最佳树种和草本植物。

关 键 词:铁尾矿  植物修复  生物量  根冠比

The research of plant selection for iron tailings repairing
Abstract:The purpose of the research is to solve the problem that not enough plants can be chosen for iron tailing repairing and the low adaptability of many plants ,w hich have preven‐ted the promotion of vegetation restoration technology .Five plants (Medicago sativ a L ., Amorpha f ruticosa L .,Gleditsia sinensis Lam .,Syringa reticulata (Blume) H .Hara var . amurensis(Rupr .)J .S .Pringle and Robinia pseudoacacia L .) were sowed directly in ground of discarded iron tailings at Malan county in Tangshan Shougang of China .The growth indices of plant height ,ground diameter ,root length ,aboveground biomass ,underground biomass and root cap ratio were measured and analyzed .The main results were as follow :Until to September 2014 the grow th condition and adaptability of Robinia pseudoacacia L .were the best among 5 plants ,the plant height of which was 77 .67 cm ,ground diameter as 6 .33 cm , root length as 23 .97 cm ,aboveground biomass as 2 040 .19 g/m2 ,underground biomass as 839 .01 g/m2 ,and the annual grow ths of the above indices all reached the maximum compare to the other plants .Except for the ground diameter index ,Medicago sativ a L .ranked as the second .The growth of Amorpha f ruticosa L .,Syringa reticulata (Blume) H .Hara var . amurensis(Rupr .)J .S .Pringle and Gleditsia sinensis Lam .were raletively poor .In Septem‐ber 2013 ,the descending order of the root cap ratios of these plants was Amorpha f ruticosa L .(1 .04) ,Gleditsia sinensis Lam .(0 .83) ,Syringa reticulata (Blume) H .Hara var .amu‐rensis(Rupr .)J .S .Pringle (0 .56) ,Robinia pseudoacacia L .(0 .37) ,and Medicago sativ a L . (0 .32) .In September 2014 ,the descending order of the plant root cap ratios was Gleditsia sinensis Lam .(1 .71) , Syringa reticulata (Blume) H .Hara var .amurensis(Rupr .)J .S . Pringle (0 .91) ,Amorpha f ruticosa L .(0 .80) ,Medicago sativa L .(0 .50) ,Robinia pseu doacacia L .(0 .41) .With the comprehensive consideration ,Robinia pseudoacacia L .is the best tree species of vegetation restoration on the tailings .Medicago sativ a L .can be used as the dominant herbaceous plant species for the restoration of iron tailings wastelands .
Keywords:iron tailing  vegetation remediation  biomass  root cap ratio
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