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Plant and Soil

, Volume 267, Issue 1–2, pp 23–40 | Cite as

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

  • Christian Huber
  • Wendelin Weis
  • Manuela Baumgarten
  • Axel Göttlein
Article

Abstract

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.

Key words

aluminium clear-cutting nitrate nutrient leaching potassium selective-cutting 

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References

  1. Adamson J K and Hornung M 1990 The effect of clearfelling a Sitka spruce (Picea sitchensis) plantation on solute concentrations in drainage water. J. Hydrol. 116, 287–297.CrossRefGoogle Scholar
  2. Ågren G I and Bosatta E 1988 Nitrogen saturation of terrestrial ecosystems. Environ. Pollut. 54, 185–197.PubMedGoogle Scholar
  3. Arthur M A Tritton L M and Fahey T J 1993 Dead bole mass and nutrients remaining 23 years after clear felling of a northern hardwood forest. Can. J. For. Res. 23, 1298–1305.Google Scholar
  4. Asner G P Scurlock J M O and Hicke J A 2003 Global synthesis of leaf area index observations: implications for ecological and remote sensing studies. Global Ecol. Biogeogr. 12, 191–205.CrossRefGoogle Scholar
  5. Bauhus J 1994 Stoffumsätze in Lochhieben. Berichte des Forschungszentrums Waldökosysteme der Univ. Göttingen, Reihe A, Bd.113 (with English summary).Google Scholar
  6. Bäumler R and Zech W 1999 Effects of forest thinning on the stream water chemistry of two forest watersheds in the Bavarian Alps. Forest Ecol. Manag. 116, 119–128.Google Scholar
  7. Berden M, Nilson S I and Nyman P 1997 Ion leaching before and after clear-cutting in a Norway spruce stand - Effects of long term application of ammonium nitrate and superphosphate. Water Air Soil Poll. 93, 1–26.Google Scholar
  8. Borman F H and Likens G E 1979 Pattern and process in a forested ecosystem: Disturbance, development and steady state based on the Hubbard Brook Ecosystem Study. Springer, New York.Google Scholar
  9. Breuer L, Eckhardt K and Frede H-G 2003 Plant parameter values for models in temperate climates. Ecol. Model. 169, 237–293.CrossRefGoogle Scholar
  10. Butterbach-Bahl K, Gasche R, Huber C, Kreutzer K and Papen H 1998 Impact of N-input by wet deposition on N-trace gas fluxes and CH4-oxidation in spruce forest ecosystems of the temperate zone in Europe. Atmos. Environ. 32, 559–564.CrossRefGoogle Scholar
  11. Butterbach-Bahl K, Gasche R, Willibald G and Papen H 2002 Exchange of N-gases at the Höglwald Forest - A summary. Plant Soil 240, 117–123.Google Scholar
  12. Cummins T and Farell E P 2003 Biogeochemical impacts of clear-felling and reforestation on blanket peatland streams. II. major ions and dissolved organic carbon. Forest Ecol. Manag. 180, 557–570.Google Scholar
  13. Dahlgren R A and Driscoll C T 1994 The effects of whole-tree clear-cutting on soil processes at the Hubbard Brook Experimental Forest, New Hampshire, USA. Plant Soil 158, 239–262.CrossRefGoogle Scholar
  14. De Keersmaeker L, Neirynck J, Maddelein D, De Schrijver A and Lust N 2000 Soil water chemistry and revegetation of a limed clearcut in a N saturated forest. Water Air Soil Poll. 122, 49–62.Google Scholar
  15. Emmett B A, Anderson J M and Hornung M 1991 The control on N-losses following two intensities of harvesting in a Sitka spruce forest (N.Wales). Forest Ecol. Manag. 41, 81–93.Google Scholar
  16. Fahey T J, Hughes J W, Pu M and Arthur M A 1988 Root decomposition and nutrient flux following whole tree harvest of northern hardwood forest. Forest Sci. 34, 744–768.Google Scholar
  17. Geßler A, Rienks M and Rennenberg H 2002 Stomatal uptake and cuticular adsorption to dry deposition of NH3 and NO2 to needles of adult spruce (Picea abies) trees. New Phytol. 156, 179–194.Google Scholar
  18. Göttlein A and Matzner E 1997 Microscale heterogeneity of acidity related stress-parameters in the soil solution of a forested cambic podzol. Plant Soil 192, 95–105.Google Scholar
  19. Hahn G and Marschner H 1998 Cation concentration of short roots of Norway spruce as affected by acid irrigation and liming. Plant Soil 199, 23–27.Google Scholar
  20. Heim A, Luster J, Brunner I, Frey B and Frossard E 2000 Effects of aluminium treatment on Norway spruce roots: Aluminium binding forms, element distribution, and release of organic substances. Plant Soil 216, 103–116.Google Scholar
  21. Huber C and Baumgarten M 2004 Early effects of forest regeneration with selective- and small scale clear-cutting on ground beetles (Coleoptera, Carabidae) in a Norway spruce stand in Southern Bavaria (Hoglwald). Biodiversity and Conservation (accepted for publication).Google Scholar
  22. Huber C and Kreutzer K 2002 Three years of continuous measurements of atmospheric ammonia concentrations over a forest stand at the Höglwald site in southern Bavaria. Plant Soil 240, 13–22.Google Scholar
  23. Huber C, Baumgarten M, Göttlein A and Rotter V 2004 Nitrogen turnover and nitrate leaching after bark beetle attack in Mountainous Spruce Stands of the Bavarian Forest National Park. Water Air Soil Poll. (in press).Google Scholar
  24. Huber C, Oberhauser A and Kreutzer K 2002 Deposition of ammonia to the forest floor canopies under spruce and beech at the Höglwald site. Plant Soil 240, 3–11.Google Scholar
  25. Johnson D W and Todd D E Jr 1998 Nutrient export by leaching and whole tree harvesting in a loblolly pine and mixed oak forest. Plant Soil 102, 99–109.Google Scholar
  26. Katzensteiner K 2003 Effects of harvesting on nutrient leaching in a Norway spruce (Picea abies Karst.) ecosystem on a Lithic Leptosol in the Northern Limestone Alps. Plant Soil 250, 59–73.CrossRefGoogle Scholar
  27. Kenk G and Guehne S 2001 Management of transformation in central Europe. For. Ecol. Manag. 151, 107–119.Google Scholar
  28. Kölling C and Prietzel J 1996 Correlations of nitrate and sulfate in the soil solution of disturbed forest ecosystems. Biogeochemistry 31, 121–128.Google Scholar
  29. Kramer P J and Boyer J S 1995 Water relations of plants and soils. Academic Press, San Diego. 493 pp.Google Scholar
  30. Kreutzer K 1995 Effects of forest liming on soil processes. Plant Soil 168-169, 447–470.Google Scholar
  31. Kreutzer K and Weiss T 1998 The Höglwald field experiment -Aims, concept and basic data. Plant Soil 199, 1–10.CrossRefGoogle Scholar
  32. Kreutzer K, Göttlein A and Pröbstle P 1991 Auswirkungen von saurer Beregnung auf den Bodenchemismus in einem Fichtenaltbestand (Picea abies [L.] Karst.)In ökosystemforschung Höglwald. Forstwiss. Forschungen 39. Eds. K Kreutzer and A Göttlein. pp. 174–186. Paul Parey Hamburg, ISBN 3-490-23916-4 (with English summary).Google Scholar
  33. Likens G E, Driscoll C T, Buso D C, Siccama T G, Johnson C E, Ryan D F, Lovett M, Fahey T and Reiners W A 1994 The biogeochemistry of potassium at Hubbard Brook. Biogeochemistry 25, 61–125.CrossRefGoogle Scholar
  34. Lindenmayer D B, Margules C R and Botkin D B 2000 Indicators of biodiversity for ecologically sustainable forest management. Conserv. Biol 14, 941–950.CrossRefGoogle Scholar
  35. Ljungström M and Stjernquist I 1995 Growth and nutrient dynamics of beech (Fagus sylvatica L.) seedlings in acid soils. Plant Soil 176, 171–181.Google Scholar
  36. Mellert K-H, Kölling C and Rehfuess K E 1996 Bioelement leaching from Norway spruce ecosystems in Bavaria after windthrow. Forstwiss. Centralbl. 115, 363–377.Google Scholar
  37. Neal C, Fisher R, Smith C J, Hill S, Neal M, Conway T, Ryland G P and Jeffrey H A 1992 The effects of tree harvesting on stream-water quality at an acidic and acid- sensitive spruce forest area: Plynlimon, mid Wales. J. Hydrol. 135, 305–319.CrossRefGoogle Scholar
  38. Neal C, Reynolds B, Wilkinson J, Hill T, Neal M, Hill S and Harrow M 1998 The impact of conifer harvesting on runoff water quality: a regional survey for Wales. Hydrol. Earth Syst. Sc. 2, 323–344.Google Scholar
  39. Parfitt R L, Salt G J and Hill L F 2002 Clear-cutting reduces nitrate leaching in a pine plantation of high natural status. Forest Ecol. Manag. 170, 43–53.Google Scholar
  40. Piirainen S, Finer L, Mannerkoski H and Starr M 2002 Effects of forest clear-cutting on the carbon and nitrogen fluxes through podzolic soil horizons. Plant Soil 239, 301–311.CrossRefGoogle Scholar
  41. Pretzsch H 1996 Growth trends of forests in Southern Germany.In Growth trends in European forests. European Forest Institute Report No.5. Eds. H Spiecker, K Mielikäinen, M Köhl and J P Skovsgaard. pp. 107–131. Springer, Berlin.Google Scholar
  42. Reynolds B and Edwards A 1995 Factors influencing dissolved nitrogen concentrations and loadings in upland streams of the U.K. Agr. Water Manage. 27, 191–202.Google Scholar
  43. Reynolds B, Stevens P A, Hughes S, Parkinson J A and Weatherly N S 1995 Stream impacts of conifer harvesting in Welsh catchment. Water Air Soil Poll. 79, 147–170.Google Scholar
  44. Richards L A 1931 Capillary conduction of liquids through porous mediums. Physics, 1, 318–333CrossRefGoogle Scholar
  45. Ring E 1995 Nitrogen leaching before and after clear-felling of fertilised experimental plots in aPinus sylvestris stand in central Sweden. Forest Ecol and Manag. 72, 151–166.Google Scholar
  46. Robertson S M C, Hornung M and Kennedy V H 2000 Water chemistry of throughfall and soil water under four tree species at Gisburn, northwest England, before and after felling. Forest Ecol. Manag. 129, 101–117.Google Scholar
  47. Röhle H 1991 Entwicklung der wichtigsten ertragskundlichen Kenngrößen des Fichtenwaldbestandes Höglwald in der 6-jährigen Beobachtungsperiode 1983–1988.)In ökosystemforschung Höglwald. Forstwiss. Forschungen 39. Eds. K Kreutzer and A Göttlein. pp. 30–34. Paul Parey, Hamburg, ISBN 3-490-23916-4 (with English summary).Google Scholar
  48. Rost-Siebert K 1983 Aluminium-Toxizität und - Toleranz an Keimpflanzen von Fichte (Picea abies Karst) und Buche (Fagus sylvatica L.). Allg. Forstztg. 38, 686–689.Google Scholar
  49. Rothe A, Huber C, Kreutzer K and Weis W 2002 Deposition and soil leaching in stands of Norway spruce and European beech: results from the Höglwald research in comparison with other European case studies. Plant Soil 240, 33–45.Google Scholar
  50. Schierl R, Göttlein A, Hohmann E, Trübenbach D and Kreutzer K 1986 Einfluß von saurer Beregnung und Kalkung auf Humusstoffe sowie die Aluminium- Schwermetalldynamik in wäßrigen Bodenextrakten. Forstwiss. Centralbl. 105, 309–313.Google Scholar
  51. Stevens P A and Hornung M 1990 Effect of harvest intensity and ground flora establishment on inorganic N-leaching from a Sitka spruce plantation in north Wales. Biogeochemistry 10, 53–65.CrossRefGoogle Scholar
  52. Ulrich B 1988 ökochemische Kennwerte des Bodens. Z. Pflanz. Bodenk. 151, 171–176.Google Scholar
  53. Ulrich B 1989 Effects of acid precipitation on forests ecosystems in Europe.In Acid precipitation. Advances in environmental science Vol 2. Eds. D C Adriano and A H Johnson. pp. 189–272. Springer, New York.Google Scholar
  54. United Nations 1992 Agenda 21: the United Nations programme of action from Rio. United Nations, New York.Google Scholar
  55. Van Miegroet H and Cole D W 1985 Acidification sources in red alder and Douglas fir soils. Importance of nitrification. Soil Sci. Soc. Am. J. 49, 1274–1279.Google Scholar
  56. Vitousek P M, Gosz J R, Grier C C, Melillo J M, Reiners W A and Todd R L 1979 Nitrate losses from disturbed ecosystems. Science 204, 469–474.Google Scholar
  57. Weis W, Huber C and Göttlein A 2001 Regeneration of mature Norway spruce stands: early effects of selective cutting on seepage water quality and soil fertility. The Sci. World 1(S2), 493–499.Google Scholar

Copyright information

© Kluwer Academic Publishers 2004

Authors and Affiliations

  • Christian Huber
    • 1
  • Wendelin Weis
    • 1
  • Manuela Baumgarten
    • 1
  • Axel Göttlein
    • 1
  1. 1.Fachgebiet für Waldernährung und Wasserhaushalt Department für Ökologie Wissenschaftszentrum Weihenstephan, TU-MünchenFreisingGermany

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