东北林业大学学报
東北林業大學學報
동북임업대학학보
Journal of Northeast Forestry University
2015年
9期
62-66
,共5页
肖欣%郭孝玉%欧阳勋志%吴自荣
肖訢%郭孝玉%歐暘勛誌%吳自榮
초흔%곽효옥%구양훈지%오자영
马尾松林%林分密度%林下植被%土壤质量
馬尾鬆林%林分密度%林下植被%土壤質量
마미송림%림분밀도%림하식피%토양질량
Pinus massoniana plantation%Stand density%Understory vegetation%Soil quality
以赣南飞播马尾松中龄林为研究对象,分别密度组Ⅰ(900~1500株· hm-2)、密度组Ⅱ(1500~2100株· hm-2)、密度组Ⅲ(2100~2700株· hm-2)、密度组Ⅳ(2700~3300株· hm-2)设置标准地,进行林下植被层基本特征调查和土壤样品测定。结果表明:灌草层平均高及草本层平均盖度均为密度组Ⅱ最大,灌木层平均盖度随着林分密度的增加而逐渐减小;不同密度组林下植被层生物量为6.53~9.84t · hm-2,从大到小的排列次序为密度组Ⅱ>Ⅲ>Ⅰ>Ⅳ,但不同密度组间差异不显著( P>0.05)。不同密度组间土壤饱和持水量、总孔隙度及全K质量分数差异显著( P<0.05),且表现为密度组Ⅱ最大,其它土壤性质指标间差异未达显著水平( P>0.05)。土壤质量综合指数依次为密度组Ⅱ(0.658)>密度组Ⅲ(03.78)>密度组Ⅰ(0.326)>密度组Ⅳ(0.261)。因此,飞播马尾松林分密度控制在1500~2100株· hm-2,有利于林下植被层的生长发育和土壤质量的提高,促进林分的正向演替。
以贛南飛播馬尾鬆中齡林為研究對象,分彆密度組Ⅰ(900~1500株· hm-2)、密度組Ⅱ(1500~2100株· hm-2)、密度組Ⅲ(2100~2700株· hm-2)、密度組Ⅳ(2700~3300株· hm-2)設置標準地,進行林下植被層基本特徵調查和土壤樣品測定。結果錶明:灌草層平均高及草本層平均蓋度均為密度組Ⅱ最大,灌木層平均蓋度隨著林分密度的增加而逐漸減小;不同密度組林下植被層生物量為6.53~9.84t · hm-2,從大到小的排列次序為密度組Ⅱ>Ⅲ>Ⅰ>Ⅳ,但不同密度組間差異不顯著( P>0.05)。不同密度組間土壤飽和持水量、總孔隙度及全K質量分數差異顯著( P<0.05),且錶現為密度組Ⅱ最大,其它土壤性質指標間差異未達顯著水平( P>0.05)。土壤質量綜閤指數依次為密度組Ⅱ(0.658)>密度組Ⅲ(03.78)>密度組Ⅰ(0.326)>密度組Ⅳ(0.261)。因此,飛播馬尾鬆林分密度控製在1500~2100株· hm-2,有利于林下植被層的生長髮育和土壤質量的提高,促進林分的正嚮縯替。
이공남비파마미송중령림위연구대상,분별밀도조Ⅰ(900~1500주· hm-2)、밀도조Ⅱ(1500~2100주· hm-2)、밀도조Ⅲ(2100~2700주· hm-2)、밀도조Ⅳ(2700~3300주· hm-2)설치표준지,진행림하식피층기본특정조사화토양양품측정。결과표명:관초층평균고급초본층평균개도균위밀도조Ⅱ최대,관목층평균개도수착림분밀도적증가이축점감소;불동밀도조림하식피층생물량위6.53~9.84t · hm-2,종대도소적배렬차서위밀도조Ⅱ>Ⅲ>Ⅰ>Ⅳ,단불동밀도조간차이불현저( P>0.05)。불동밀도조간토양포화지수량、총공극도급전K질량분수차이현저( P<0.05),차표현위밀도조Ⅱ최대,기타토양성질지표간차이미체현저수평( P>0.05)。토양질량종합지수의차위밀도조Ⅱ(0.658)>밀도조Ⅲ(03.78)>밀도조Ⅰ(0.326)>밀도조Ⅳ(0.261)。인차,비파마미송림분밀도공제재1500~2100주· hm-2,유리우림하식피층적생장발육화토양질량적제고,촉진림분적정향연체。
With the soil sample data of different stand density groups of Ⅰ ( 900-1 500 N · hm-2 ) , Ⅱ ( 1 500-2 100 N · hm-2),Ⅲ(2 100-2 700 N· hm-2), and Ⅳ(2 700-3 300 N· hm-2) in middle-aged aerially-seeded Pinus massoniana plantation in south of Jiangxi Province , we explored the effect of stand density on the understory vegetation and soil quality . The understory layer average height and herb layer average coverage of density group Ⅱ were the largest , and the average coverage of shrub layer was decreased with the increase of stand density .The biomass of understory vegetation layer be-tween different densities was in 6.53-9.84 t· hm-2 , with the descending order of Ⅱ,Ⅲ, Ⅰand Ⅳ, but the differences between density groups were not significant( P>0 .05) .The differences of soil saturated water holding capacity , total poros-ity and total K content of different density groups were significant (P<0.05), and the density group Ⅱ was the highest. The differences between other indicators of soil properties were not significant ( P>0.05).The descending order of soil quality comprehensive indexs was Ⅱ(0.658), Ⅲ (0.378), density groupⅠ(0.326), and density group Ⅳ (0.261). Therefore, controlling the stand density of aerially seeded Pinus massoniana plantation in 1 500-2 100 N· hm-2 would be helpful for the growth of understory vegetation layer , the soil quality , and positive stand succession .