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1.
根据5a定位观测,对尖峰岭热带山地雨林更新林生态系统的水文化学循环规律数据分析表明,年均降雨量为2668.3mm,其中总径流量占46.7%,蒸散量53.3%,冠层留量14.0%。N、P、K、Ca、Mg的年均降雨输入量为78.4kg(hm^2.a),总径流输出56.7kg/(hm^2.a),净积累21.6kg/(hgm^2.a),Si,有机C、Al、Mn的年均降雨输入量为25.0kg(hm^2.a) 相似文献
2.
清澜港的红树林在保护较好的条件下具有乔灌两层,乔木层高4~8m,灌木层高0.4~1.2m。上层立木地上部分生物量垂直分布随树体部位增高而减少,0~2m占50%,2~4m占40.3%,4m以上占9.7%。乔木群落被破坏后,面积锐减,27a减少1611hm2,且形成仅有单层结构的灌丛,其生物量和生产力很低,分别为9.6~14.3t/hm2和1.1~2.0t/(hm2·a)。本项研究测定了木榄林的生物量和净生产量分别为91.5t/hm2和4.7t/(hm2·a),预测以后第6年的生物量和年净生产量将是350.7t/hm2和13.5t/(hm2·a),为红树林造林和经营提供了理论依据。 相似文献
3.
不同龄组马尾松人工林生物量及生产力的研究 总被引:3,自引:0,他引:3
刘茜 《中南林业科技大学学报(自然科学版)》1996,(4)
对桂中丘陵区不同龄组马尾松人工林的生物量及生产力进行了研究.结果表明:幼龄林(8a生)生物量为32.0t/hm2,中龄林(14a生〕为108.0t/hm2、近熟林(23a生)为186.6t/hm2,成熟林(38a生)为197.4t/hm2;林分平均净生产量分别为4.00t/hm2·a.7.71t/hm2·a、8.12t/hm2·a和5.80t/hm2·a. 相似文献
4.
采用径流小区定位观测法,对保山砂页岩发育的山地红壤进行不同整地方式营造蓝桉林,经过三年的监测研究表明:未整地自然土壤侵蚀量达1.657~1.402t/hm2·a,有机质流失量达80.483~68.113kg/hm2·a,土壤肥力退化显著;撩壕整地及挖塘整地造林当年土壤侵蚀量分别达3.366t/hm2·a及2.464t/hm2·a,均属轻度侵蚀级,第二年土壤侵蚀量为0.592t/hm2·a及0.367t/hm2·a为微度侵蚀。有机质流失量为75.811kg/hm2·a及47.122kg/hm2·a。随着桉树幼林生长,林地覆盖度和地表稳定程度增加,土壤侵蚀急剧下降。 相似文献
5.
哀牢山木果石栎林降雨过程中的养分循环 总被引:1,自引:0,他引:1
本文以云南哀牢山国家级自然保护区中山湿性常绿阔叶林的主要森林类型-木果石栎林为研究对象,分析了大气降雨对该生态系统地养分循环。结果表明,以大气降雨,穿透雨和树木干流为养分输入,以地表迳流和土壤渗漏为养分输出的养分循环过程中N、P、K,Ca等分别增加了15.941kg/hm^2.a,0.353kg/hm^2.a,3.83kg/hm^2.a和1.201kg/hm^2.a而Mg减少了0.654kg/hm 相似文献
6.
本文以云南哀牢山国家级自然保护区中山湿性常绿阔叶林的主要森林类型——木果石栎林为研究对象,分析了大气降雨对该生态系统的养分循环。结果表明,以大气降雨、穿透雨和树木干流为养分输入,以地表迳流和土壤渗漏为养分输出的养分循环过程中,N、P、K、Ca等分别增加了15.941kg/hm~2·a,0.353kg/hm~2·a,3.83kg/hm2·a和1.201kg/hm~2·a,而Mg减少了0.654kg/hm~2·a。 相似文献
7.
1982~1991年,对广西宜山县庆远林场不同整地方式及其不同植被类型的水文要素进行对比观测研究。结果表明,梯形整地桉松混交林模式具有显著的涵养水源、保持水土功能;与其他植被类型相比较,具有以下几点显著的差异:a.森林群落冠层的年截留水量为230.1mm,占降水量的18.4%,比其他森林群落增加截留量12.0%~57.1%。b.枯枝落叶层贮量及其最大持水量分别为7.7t/hm2和23.0t/hm2,是其他植被类型的1.4~6.4倍。c.土壤层的最大贮水量为511.5mm,比其他植被类型增加贮水6.6%~11.8%。d.林地水、土流失量分别为4.6m3/(hm2·a)和0.63kg/(hm2·a),比其他植被类型减少79.0%~97.9%。 相似文献
8.
蜡蚧轮枝菌用湿地松粉蚧连续复壮2~3次后,用其防治湿地松粉蚧,杀虫效果可提高12.3%以上,筛选出轮枝菌复合剂的最优配方为轮枝菌0.3亿/ml加机油乳剂1:28.6(机油乳剂:水)及适量增效剂、悬浮剂及轮枝菌0.25亿/ml加机油乳剂1:80及增效剂。悬浮剂,它们室内杀虫效果分别为92.8%和83.5%。林间采用轮枝菌151亿/hm2加机油乳剂0.75kg/hm2和轮枝菌15万亿/hm2加机油乳剂3.75kg/hm2,喷洒量为10kg/hm2,越冬代粉蚧(成虫)的死亡率分别为48.5%和71.2%,第一代粉蚧(若虫、成虫)的死亡率分别为99.3%和92.7%。越冬后期喷菌,第一代的虫口密度比未喷菌区下降52.7%;采用液、固双相发酵工艺生产的轮枝菌含孢量达55亿/g,比前人用高梁、小米作培养基密封培养的产孢量(4.1亿/g)提高了12.4倍,成本为3.38元/kg,此工艺流程可以推广应用。 相似文献
9.
内蒙古磴口河套地区4a灌溉试验表明:(1)采用目前生产上的15000-22500m^3/(hm^2.a)灌溉量,使土壤表层的含盐量由灌溉前的0.5g/kg上升到1.0g/kg以上。(2)按合理灌水定额公式计算,年灌溉量以7500m^3/hm^2为宜;最佳含水率下限19.99%;在灌水期地下水位为1.97-3.02m,变幅1m左右(3)年灌水次数应控制在8-12次。 相似文献
10.
杉木幼林生态系统N,P,K循环及模拟研究 总被引:6,自引:0,他引:6
在尤溪杉木人工林生态站7年定位观测基础上,进行杉木幼林生态系统养分循环研究,建立了养分循环的分室模型。结果表明:7年生杉木幼林生态系统N、P、K贮量分别为;7308.46、2022.96、130290.14kg/nm2,其中99.73%存在于土壤分室中。杉木幼林N、P、K年吸收量52.20kg/hm2,年存留量22.62kg/hm2,年归还量29.58kg/hm2,系统每年通过水文学途径获得N、P、K为15.92kg/hm2,径流输出9.23kg/hm2,系统中年净积累6.69kg/hm2。同时通过计算模拟,定量地描述了0—10年内系统N、P、K在各分室的运转状态及施肥效果,并计算了N、P、K达到稳定状态时的平衡点。 相似文献
11.
The role of canopy interception on nutrient cycling in Chinese fir plantation ecosystem was studied on the basis of the position
data during four years. Results indicate that the average canopy interception amount was 267.0 mm/year. Canopy interception
play a significant role in water cycle and nutrient cycle processes in ecosystem, and was an important part of evaporation
from the Chinese fir plantation ecosystem, being up to 27.2%. The evaporation from the canopy interception was an important
way of water output from ecosystem, up to 19.9%. The flush-eluviation of branches and leaves caused by canopy interception
brought nutrient input of 143.629 kg/(hm2 · year), which was 117.2% of the input 63.924 kg/(hm2 · year) from the atmospheric precipitation. The decreased amount of 80.1 mm precipitation input caused by canopy interception
reduced the amount of rainfall into the stand surface and infiltration into the soil, reduced the output with runoff and drainage,
and decreased nutrient loss through output water. Therefore, the additional preserve of nutrient by canopy interception was
8.664 kg/(hm2 · year).
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Translated from Scientia Silvae Sinicae, 2006, 42(12): 1–5 [译自: 林业科学] 相似文献
12.
Zhenhong Wang Chengbo Yang Limei Yang Zizong Zhou Jing Rao Li Yuan Ju Li 《Frontiers of Forestry in China》2007,2(1):18-27
In recent years, the relationship between biodiversity and ecosystem stability, productivity, and other ecosystem functions
has been extensively studied by using theoretical approaches, experimental investigations, and observations in natural ecosystems;
however, results are controversial. For example, simple systems were more stable than complex systems in theoretical studies,
and higher productivity was observed in human-made ecosystems with poorer species composition, etc. The role of biodiversity
in the ecosystem, such as its influence on sustainability, stability, and productivity, is still not understood. Because accelerated
soil-erosion in various ecosystems has caused a decrease of primary productivity, a logical way used in the study of the relationship
between biodiversity and ecosystem function can be used to study the relationship between plant species diversity and soil
conservation. In addition, biodiversity is a product of evolutionary history, and soil erosion is a key factor controlling
the evolution of modern environment on the surface of the Earth. A study on the relationship between biodiversity and soil-erosion
processes could help us understand the environmental evolution of Earth.
Fifteen 10 m × 40 m standard runoff plots were established to measure surface runoff, soil erosion, and total P loss in different
secondary communities of semi-humid evergreen broad-leaved forests that varied in composition, diversity, and level of disturbance
and soil erosion. The following five communities were studied: AEI (Ass. Elsholtzia fruticosa + Imperata cylindrical), APMO (Ass. Pinus yunnanensis + Myrsine africana + Oplismenus compsitus), APLO (Ass. Pinus yunnanensis + Lithocarpus confines + Oplismenus compsitus), AEME (Ass. Eucalyptus smith + Myrsine africana + Eupatorium adenophorum), and ACKV (Ass. Cyclobalanopsis glaucoides + Keteleeria evelyniana + Viola duelouxii). Tree density, the diameter of the tree at breast height, and the hygroscopic volume of plant leaves were determined in
each plot.
Results indicated that surface runoff, soil erosion, and total P loss decreased as a power function with increase in plant
species diversity. Their average values for three years were 960.20 m3/(hm2 · year), 11.4 t/(hm2 · year), and 127.69 kg/(hm2 · year) in the plot with the lowest species diversity, and 75.55 m3/(hm2 · year), 0.28 t/(hm2 · year), and 4.71 kg/(hm2 · year) in the plot with the highest species diversity, 12, 50, and 25 times respectively lower compared with the lowest
species diversity plots. The coefficients of variation of surface runoff, soil erosion, and total P loss also followed a power
function with the increase of plant species diversity, and were 287.6, 534.21, and 315.47 respectively in the lowest species
diversity plot and 57.93, 187.94, and 59.2 in the highest species diversity plot. Enhanced soil conservation maintained greater
stability with increased plant species diversity. Plant individual density increased linearly and the canopy density and cross
section at breast height increased logarithmically with the increase of plant species diversity. The hydrological function
enhanced as the plant species diversity increased. There were obviously relationships between plant species diversity and
rainfall interception, coverage, and plant individual density, which was related to soil conservation functions in the five
forest communities.
The complex relationships between plant species diversity and the above-mentioned ecological processes indicated that plant
species diversity was an important factor influencing the interception of rainfall, reducing soil erosion and enhancing the
stability of soil conservation, but its mechanism is not known. This experiment showed that plant species diversity promoted
soil and nutrient conservation and ultimately lead to the increase of the primary productivity of the ecosystem, and was thus
a good way to study the relationship between biodiversity and ecosystem stability. Rainfall interception could be assessed
easily using the hygroscopic volume of plant leaves. Because there were strong correlations between plant species diversity
and soil conservation functions, the patterns of plant species diversity will show a certain level of predictability on the
interactions of life systems with surface processes of the Earth.
__________
Translated from Journal of Plant Ecology, 2006, 30(3): 392–403 [译自: 植物生态学报 相似文献
13.
Forest precipitation chemistry is a major issue in forest hydrology and forest ecology. Chemical contents in precipitation
change significantly when different kinds of external chemical materials are added, removed, translocated and transformed
to or in the forest ecosystem along with precipitation. The chemistry of precipitation was monitored and analyzed in a 31-year-old
Pinus tabulaeformis forest in the West Mountain of Beijing. Movement patterns of nutrient elements in hydrological processes can be discovered
by studying this monitored data. Also, the information is useful for diagnosing the function of ecosystems and evaluating
the impact of the environment on the ecosystem.
Samples of rainfall, throughfall and stemflow were collected on the site. In the lab, Ca2+ and Mg2+ were analyzed by flame atomic absorption and K+ and Na+ by flame emission. NH4
+-N was analyzed by indophenol blue colorimetry and NO3
−-N was analyzed by phenoldisulfonic acid colorimetry. The results showed that: 1) The concentration gradient of nutrient elements
clearly changed except for Na+. The nutrients in stemflow were significantly higher than those of throughfall and rainfall as the precipitation passed through
the P. tabulaeformis forest. The monthly patterns showed distinct differentiation. There are indications that a large amount of nutrients was
leached from the canopy, which is a critical function of intra-ecosystem nutrient cycling to improve the efficiency of nutrient
use. 2) The concentrations of NO3
−-N and K+ changed more than those of the other nutrient elements. The concentration of NO3
−-N in throughfall and stemflow was 4.4 times and 9.9 times higher than those in rainfall, respectively. The concentration
of K+ in throughfall and stemflow was 4.1 times and 8.1 times higher than those in rainfall, respectively. 3) The leaching of nutrient
elements from the stand was an important aspect of nutrient return to the P. tabulaeformis forest, which returned a total amount of nutrient of 54.1 kg/hm2, with the contribution of Ca2+ and K+ much greater than that of other elements. Also, K+ was the most active element in leaching intensity. 4) Nutrient input through precipitation was the main source in the West
Mountain of Beijing and the amount of nutrient added was 66.4 kg/hm2, of which Ca2+ and N contributed much more than the other nutrient elements. When precipitation passes through the P. tabulaeformis forest, 121 kg/hm2 of nutrient is added to the forest floor. Ca2+ recorded the greatest nutrient increase, with 61.2 kg/hm2, followed by N (NH4
+-N and NO3
−-N), K+ and Mg2+, with 31.3 and 16.5, and 8.11 kg/hm2, respectively. The least was Na+, 3.34 kg/hm2.
Translated from Acta Ecologica Sinica, 2006, 26(7): 2,101–2,107 [译自: 生态学报] 相似文献
14.
1984~1996年在江西分宜县中国林科院亚热带林业实验中心的3个林场,分别对杉木人工林幼龄林、中龄林及近熟林进行了8组水土保持及养分循环方面多点的试验观测,对杉木人工林水土流失及养分损耗作了研究。结果表明,杉木人工林水土流失以幼林阶段为最大,其次中龄林阶段,最小是近熟林阶段。幼龄林地表迳流量为546.0m^3.hm^-2,土壤侵蚀总量为1050.0kg.hm^-2,土壤侵蚀量尤为明显;中龄林地表迳流量为506.98m^3.hm^-2;而近熟林地表迳流量为477.25m^3.hm^-2,土壤侵蚀量可略而不计。幼龄林流失有机质50.049kg.hm^-2,养分为31.508kg.hm^-2;中龄林流失有机质为6.080kg.hm^-2,养分流失量为2.096kg.hm^-2,而近熟林养分流失量为10.784kg. 相似文献
15.
Mingdong Ma Chengde Luo Hong Jiang Yuejian Liu Xi Li 《Frontiers of Forestry in China》2009,4(2):140-145
Biomass, carbon content, carbon storage and spatial distribution in the 32-year-old Phoebe bournei artificial forest were measured. The mean biomass of the forest stand was 174.33 t/hm2, among which the arbor layer was 166.73 t/hm2, which accounted for 95.6%. Carbon contents of stems, barks, branches, leaves, root, shrub layer, herb layer, lichen layer
and litter layer were 0.5769 g C/g, 0.4654 g C/g, 0.5232 g C/g, 0.4958 g C/g, 0.4931 g C/g, 0.4989 g C/g, 0.4733 g C/g, 0.4143
g C/g, 0.3882 g C/g, respectively. The mean carbon content of soil was 0.0139 g C/g, which reduced gradually along with soil
depth. Total carbon storage of the P. bournei stand ecosystem was 227.59 t/hm2, among which the arbor layer accounted for 40.13% (91.33 t/hm2), the shrub layer accounted for 0.17% (0.38 t/hm2), the herb layer accounted for 0.76% (1.71 t/hm2), the lichen layer accounted for 0.28% (0.63 t/hm2), and the litter layer accounted for 0.29% (0.66 t/hm2). Carbon content (0–80 cm) of the forest soil was 58.40% (132.88 t/hm2). Spatial distribution ranking of carbon storage was: soil layer (0–80 cm) > arbor layer > herb layer > litter layer > lichen
layer > shrub layer. Net production of the forest stand was 8.5706 t/(hm2·a), in which the arbor layer was 6.6691 t/(hm2·a), and it accounted for 77.82%. Net annual carbon sequestration of the P. bournei stand was 4.2536 t/(hm2·a), and the arbor layer was 3.5736 t/(hm2·a), which accounted for 84.01%.
__________
Translated from Scientia Silvae Sinicae, 2008, 44(3): 34–39 [译自: 林业科学] 相似文献
16.
17.
The functions of canopy interception on energy conversion processes in a Chinese fir plantation ecosystem were studied with
the aid of long-term observation data in Huitong. The results showed that the absorbed, penetrated and reflected amounts of
solar radiation were, respectively, 2.5543 × 109 J/(m2·year) (absorption rate of 0.827), 2.5306 × 108 J/(m2·year) (penetration rate of 0.082), and 2.7432 × 108 J/(m2·year) (reflection rate of 0.091) by the canopy. The conversion of net solar radiation to latent heat in the process of evaporation
from canopy interception amounted to 6.3695 × 108 J/(m2·year) (accounting for 22.9% of total ecosystem net radiation and 30.4% of ecosystem evaporation), which was an important
part of the budget of the energy system. Canopy interception consumed kinetic energy of raindrops in overcoming resistance
of branches and leaves, which collected raindrops, followed with the conversion of potential energy in raindrops to kinetic
energy with falling raindrops. In general, the diameter of raindrops from the canopy is larger than that of the raindrops
above the canopy as a result of the collection effort by the canopy. The kinetic energy of raindrops from the canopy, therefore,
was higher than that of raindrops in the atmosphere. The drop-size distribution from the canopy was affected by the structure
of the canopy layer rather than the amount of precipitation and precipitation intensity. The canopy had no important nor efficient
effects on decreasing the kinetic energy of raindrops in our case study with a first branch height of 7 m and precipitation
amounts over 3 mm. However, the canopy would play a key role in decreasing kinetic energy of raindrops in two cases, that
of a small amount of precipitation and one of heavy precipitation intensity, in which the canopy could intercept the largest
amount of precipitation in the former condition and the canopy could scatter bigger raindrops to smaller raindrops with striking
leaves in the case of heavy precipitation.
__________
Translated from Scientia Silvae Sinicae, 2007, 43(2): 15–20 [译自: 林业科学] 相似文献
18.
湖南第2代杉木幼林的水文学过程及养分动态研究 总被引:8,自引:2,他引:8
采用小集水区技术和定位研究方法 ,根据连续 3a观测所取得的数据 ,对湖南会同第 2代杉木幼林的水量平衡和养分元素的地球化学循环进行了研究。结果表明 :该森林生态系统年降雨输入为 1170 6mm ,其中 3 5 3mm以树干茎流形式进入林地 ,占降雨量的 0 3% ,林内穿透水为 10 17 3mm ,占 86 9% ,另外林冠年截留量为 149 77mm ,占年降雨量的 12 8%。以径流形式流出该系统的水量为 42 8 0 5mm ,占年降雨量的 36 5 7% ,其中地表径流和地下径流分别占总径流的 4 31%和 95 6 9%。系统另一输出形式蒸散量为 86 2 6 4mm ,为年降雨量的 6 2 2 %。在该森林生态系统中 ,由降雨输入的N、P、K、Ca、Mg等元素的总量为 5 3 173kg·hm- 2 ·a- 1 ,径流输出量为 42 5 6 3kg·hm- 2 ·a- 1 ,净积累量为 10 6 10kg·hm- 2 ·a- 1 。与稳定态的第 1代杉木林相比 ,第 2代杉木幼林的林冠截留量成倍减少 ,地表径流、地下径流量和径流总量都高于第 1代杉木林 ,其涵养水源的能力相对较弱 ,抵抗外界干扰的能力比稳定态的第 1代杉木林差。从生物循环来看 ,第 2代杉木幼林的养分存留量大 ,表明第 2代杉木幼林将从土壤中吸收的养分大量地保存在林木中 ,造成土壤中养分的逐渐减少 ,维持持久的林地生产力应引起重视。第 2代杉木幼林 相似文献
19.
Xingliang Liu Qinyan Ma Dongsheng Yang Zuoming Shi Yiming Su Shiqiang Zhou Shirong Liu Yupo Yang 《Frontiers of Forestry in China》2006,1(4):379-386
This study investigated root biomass and productivity in dominant populations in western Sichuan, China. A total of 4 plots
(Picea balfouriana plantation for 22 age in Maerkang, 9 trees, mean DBH of population for 10.4 cm and height for 10.5 m; Larix maxteriana plantation for 22 age in Wolong, 9 trees, mean DBH of population for 17.0 cm and height for 13.8 m; Abies fabri plantation for 35 age in Ebian, 18 trees, mean DBH of population for 14.1 cm and height for 11.9 m; Larix kaempferi plantation for 23 age in Miyaluo, 8 trees, mean DBH of population for 17.4 cm and height for 14.5 m; a 20 m×25 m plot located
on each of the 4 types in western Sichuan, China) were randomly selected and excavated to a depth of 60 cm for each of the
4 plantation types. To estimate the root biomass of an individual tree using D
2
H, an exponential model was selected with the highest coefficient ranging from 0.94 to 0.99. The total root biomass per hm2 varied among plantation population types following the order: L. kaempferi (37.832 t/hm2) > A. fabri (24.907 t/hm2) > L. maxteriana (18.320 t/hm2) > P. balfouriana (15.982 t/hm2). The biomass fractions of a given root size class compared to the total root biomass differed among plantation population
types. For all 4 studied plantation types, the majority of the roots were distributed in the top 40 cm of soil, e.g., 97.88%
for P. balfouriana population, 96.78% for L. maxteriana, 95.65% for A. fabri, and 99.72 for L. kaempferi population. The root biomass fractions distributed in the top 20 cm of soil were 77.13% for P. balfouriana, 77.13% for L. maxteriana, 65.02% for A. fabri and 80.66% for L. kaempferi, respectively. The root allocation in the 0–20, 20–40, and 40–60 cm soil layers gave ratios of 34:12:1 for P. balfouriana, 24:6:1 for L. maxteriana, 15:7:1 for A. fabri, and 64:4:1 for L. kaempferi populations. The root biomass density of dominant plantation population was 10.782 t/(hm2·m) for P. balfouriana, 8.230 t/hm2·m) for L. maxteriana, 24.546 t/(hm2·m) for A. fabri, and 13.211 t/(hm2·m) for L. kaempferi population, respectively. The root biomass productivity was found to be 0.57 t/(hm2·year) for P. balfouriana, 0.83 t/(hm2·year) for L. maxteriana, 0.71 t/(hm2·year) for A. fabri and 1.64 t/(hm2·year) for L. kaempferi population, respectively.
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Translated from Acta Ecologica Sinica, 2006, 26(2): 542–551 [译自: 生态学报, 2006, 26(2): 542–551] 相似文献