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Spatial and temporal variation of seepage water chemistry after femel and small scale clear-cutting in a N-saturated Norway spruce stand

机译:N饱和的挪威云杉林中粉刺和小规模明晰切割后渗流水化学的时空变化

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摘要

The chemistry of seepage water was studied before and after small scale clear-cutting and femel cutting (removing 20% of the trees) between 1999 and 2002 at the Höglwald site in southern Bavaria. The interventions were performed in February 2000 on mature, N-saturated Norway spruce (Picea abies (L.) Karst.) stands with high NO 3 − concentrations before felling. Seepage water was collected with suction cups at 40 cm soil depth in the following treatments: (I) a mature stand (control), (II) a femel-cut, and (III) a clear-cut. In the femel cut subvariants were created with suction cups (plots) at varying distances from pre-selected spruce, which were later removed. The femel treatment was replanted with beech (Fagus sylvatica L.) saplings. On the clear-cut, subvariants of planted beech (close to the stem, interstem area), planted spruce (interstem), or natural spruce regeneration were investigated. Clear-cutting caused high NO 3 − peaks (average values up to 2750 µM) during 2000 and 2001 in all planted tree subvariants during times of comparatively low water fluxes. In contrast to peak concentrations, flux weighted yearly average concentrations showed different trends. In 2000, flux weighted yearly average NO 3 − concentrations were significantly elevated, but only on the subvariants of the interstem area, which covered in the clear-cut plot ca. 62% of the area. However, the subvariant close to the stem (31% of clear-cut area), or the natural spruce regeneration subvariant (6% of clear-cut area) exhibited no significant felling effect. With respect to the whole treatment area, this resulted in no significant felling effect as compared with the control. In the next year (2001), flux weighted yearly average NO 3 − concentrations were not significantly affected by clear-cutting, while the concentrations were even reduced for all of the clear-cut subvariants in 2002. On the subvariant natural spruce regeneration, NO 3 − concentrations remained below the European limit of drinking water (806 µM) during almost the whole investigation period. Selective cutting resulted in slightly reduced NO 3 − concentrations in 2000 and 2001 on the femel treatment. However, no significant effect could be detected for any subvariant in the femel-cut, even not for the subvariant with suction cups closest to the felled spruce. In contrast to many other investigations, clear-cutting did not increase the NO 3 − problem on the treatment to a relevant extend. Quite contrary, a decline in NO 3 − concentrations to values below the EU level for drinking water and levels below the control and femel treatment just 2 years after cutting were observed. Al3+ concentrations showed nearly the same trend as NO 3 − , while Ca2+, Mg2+, and K+ concentrations were affected to a lesser degree. Only in 2002 was Ca2+ significantly lower on the clear-cut as compared to the femel treatment, but not compared to the control. Mg2+ increased in 2000 on the clear-cut subvariants in the interstem area, but decreased in the years 2001 and 2002. Changes could be observed for K+ only periodically on some subvariants, but not for the whole treatment area. Concentrations of SO 4 2− , Na+, and Cl− were reduced after clear-cutting and remained nearly unchanged after femel cutting.
机译:在1999年至2002年间,在巴伐利亚南部的Höglwald工地进行了小规模的整枝砍伐和费莫尔砍伐(砍伐了20%的树木)之前和之后的渗水化学研究。干预于2000年2月对成熟的,氮饱和的挪威云杉(Picea abies(L.)Karst。)林木进行砍伐之前,这些林木中NO 3的浓度较高。在以下处理中,用吸盘在土壤深度40 cm处收集渗水:(I)成熟林分(对照),(II)淡粉切割,(III)透明切割。在femel切割的切割中,通过与距预先选定的云杉不同距离的吸盘(图)创建了子变量,随后将其移除。 Femel处理再植以山毛榉(Fagus sylvatica L.)树苗。在明确的地方,调查了种植的山毛榉(靠近茎,茎间区域),种植的云杉(茎间)或自然云杉再生的亚变种。在2000年和2001年期间,在通水量较低的情况下,所有种植的树木亚变种均产生了较高的NO 3 -峰值(平均值高达2750 µM)。与峰值浓度相反,通量加权的年平均浓度显示出不同的趋势。在2000年,通量加权的年平均NO 3 -浓度显着升高,但仅在跨界区域的子变量上,该区域被清晰的图约所覆盖。面积的62%。但是,靠近茎的亚变种(纯净面积的31%)或自然云杉再生亚变种(纯净面积的6%)没有明显的采伐效果。对于整个治疗区域,与对照相比没有明显的砍伐效果。在第二年(2001年),通量加权对NO 3 -的年平均浓度没有明显影响,而在2002年,所有明晰亚变量的浓度甚至降低了。在亚自然云杉再生方面,几乎在整个调查期间,NO 3 -的浓度均保持在欧洲饮用水限值(806 µM)以下。通过选择性切割,Femel处理在2000年和2001年导致NO 3 -浓度略有降低。但是,对于femel-cut中的任何亚变种,即使对于最接近采伐云杉的吸盘的亚变种,也无法检测到显着效果。与许多其他研究相反,明确的处理并没有在一定程度上增加NO 3 -问题。恰恰相反,观察到切割后仅2年,NO 3的浓度降低到饮用水的EU值以下和对照和Femel处理的水平以下。 Al3 + 浓度与NO 3 -趋势几乎相同,而Ca2 + ,Mg2 + 和K + 浓度受到的影响较小。 。仅在2002年,与Femel处理相比,纯净形式的Ca2 + 明显降低,但与对照相比则没有。 Mg2 + 在中间区域的明确亚变种中在2000年有所增加,但在2001年和2002年有所下降。在某些亚变种中,仅周期性地观察到K + 的变化,但在整个处理过程中观察不到区域。透明切割后,SO 4 2 − ,Na + 和Cl-的浓度降低,而在费米尔切割后保持几乎不变。

著录项

  • 来源
    《Plant and Soil》 |2004年第2期|23-40|共18页
  • 作者单位

    Fachgebiet für Waldernährung und Wasserhaushalt Department für Ökologie Wissenschaftszentrum Weihenstephan TU-München;

    Fachgebiet für Waldernährung und Wasserhaushalt Department für Ökologie Wissenschaftszentrum Weihenstephan TU-München;

    Fachgebiet für Waldernährung und Wasserhaushalt Department für Ökologie Wissenschaftszentrum Weihenstephan TU-München;

    Fachgebiet für Waldernährung und Wasserhaushalt Department für Ökologie Wissenschaftszentrum Weihenstephan TU-München;

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  • 原文格式 PDF
  • 正文语种 eng
  • 中图分类
  • 关键词

    aluminium; clear-cutting; nitrate; nutrient leaching; potassium; selective-cutting;

    机译:铝;透明;硝酸盐;养分浸出;钾;选择性切割;

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