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Accumulation of soil organic C and change in C:N ratio after establishment of pastures on reverted scrubland in New Zealand

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Abstract

Rates of organic carbon accumulation and changes in C:N ratio are reported for 10 New Zealand soils converted to pastures from scrub. The data were derived from archive papers originally published in 1964, but which did not report on changes in the C contents of the soils. The soils had been sampled to 0–7.5, 7.5–15, and 15–30 cm depths and chronosequences of up to 66 years obtained by selecting sites with differing times since pasture establishment. We calculated changes in the mass of C and N in the 0–7.5 cm depth and compared that to the mass in the 0–30 cm depth of soil. The shortest time over which organic matter change was assessed was 18 years and the longest was 66 years. Nine of the ten soils showed increases in the C contents of the 0–7.5 cm depth soil, and a natural logarithmic curve generally gave a better fit to the time course data than a linear fit. However, when the full 0–30 cm depth was considered, only two soils showed a significant increase in total C, changes in the C contents of other soils were non-significant, and two soils showed a decline in total C. The rates of change in the C contents were averaged over 0–5 years, 5–25 years and 25–50 years. Across all 10 soils, the mean rates of accumulation of C in the 0–7.5 cm depth were 1.07 (between 0 and 5 years), 0.27 (between 5 and 25 years) and 0.09 Mg C ha−1 year−1 (between 25 and 50 years) and significantly (P < 0.05) greater than zero. Very similar rates were obtained for the 0–30 cm depth of soil with mean rates across all soils 1.01 (0–5 years), 0.25 (5–25 years) and 0.09 Mg C ha−1 year −1 (25–50 years), respectively. In the 0–7.5 cm depth of soil, total Kjeldahl N (TKN) increased significantly in seven of the 10 soils. When expressed for the 0–30 cm depth of soil, only five soils still showed significant increases in TKN contents over time. Using the data for the 0–7.5 cm depth, the predicted time (mean and standard error) for the soils to reach a C:N ratio of <10 was 46 ± 17 years. The soils were originally sampled over 44 years ago, suggesting that currently (2009), very few of them could be expected to have capacity for further N storage in organic matter in the surface soil unless there was an increase in soil C. Changes in soil C and N in the shallow upper soil layers are easily masked by the relatively small changes in C and N contents and much greater masses of soil at lower depths.

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References

  • Batjes NH (1996) Total carbon and nitrogen in soils of the world. Eur J Soil Sci 47:151–163

    Article  Google Scholar 

  • Blanco-Canqui H, Lal R (2008) No tillage and soil profile carbon sequestration: an on-farm assessment. Soil Sci Soc Am J 72:693–701

    Article  Google Scholar 

  • Conant RT, Paustian K (2002) Spatial variability of soil organic carbon in grasslands: implications for detecting change at different scales. Environ Pollut 116:S127–S135

    Article  Google Scholar 

  • Conant RT, Paustian K, Elliott T (2001) Grassland management and conversion into grassland: effects on soil carbon. Ecol Appl 11:343–355

    Article  Google Scholar 

  • Conant RT, Paustian KP, Del Grosso SJ, Parton W (2005) Nitrogen pools and fluxes in grassland soils sequestering carbon. Nutr Cycl Agroecosyst 71:239–248

    Article  Google Scholar 

  • Conant RT, Easter M, Paustian K, Swan A, Williams S (2007) Impacts of periodic tillage on soil C stocks: a synthesis. Soil Tillage Res 95:1–10

    Article  Google Scholar 

  • Francis GS, Tabley FJ, White KM (1999) Restorative crops for the amelioration of degraded soil conditions in New Zealand. Aust J Soil Res 37:1017–1034

    Article  Google Scholar 

  • Galloway JN, Aber JD, Erisman JW, Speitsinger SP, Howarth RW, Cowing EB, Cosby BJ (2003) The nitrogen cascade. Bioscience 53:341–356

    Article  Google Scholar 

  • Gregorich EG, Carter MR (1997) Soil quality for crop production and ecosystem health. Developments in Soil Science 25. Elsevier, Amsterdam

    Google Scholar 

  • Hart PBS, West AW, Kings JA, Watts HM, Howe JC (1999) Land restoration management after topsoil mining and implications for restoration policy guidelines in New Zealand. Land Degrad Dev 10:435–453

    Article  Google Scholar 

  • Hewitt AE (1998) New Zealand soil classification. Manaaki Whenua Press, Landcare Research, Lincoln

  • Jackman RH (1964a) Accumulation of organic matter in some New Zealand soils under permanent pasture. I. Patterns of change of organic carbon, nitrogen, sulphur and phosphorus. N Z J Agric Res 7:445–471

    Google Scholar 

  • Jackman RH (1964b) Accumulation of organic matter in some New Zealand soils under permanent pasture. II. Rates of mineralization of organic matter and the supply of available nutrients. N Z J Agric Res 7:472–479

    Google Scholar 

  • Jenkinson D, Hart PBS, Rayner JH, Parry LC (1987) Modelling the turnover of organic matter in long-term experiments at Rothamsted. INTECOL Bull 15:1–8

    Google Scholar 

  • Parliamentary Commissioner for the Environment (2004) Growing for good. Intensive farming, sustainability and the New Zealand environment. Parliamentary Commissioner for the Environment, Wellington, 236 pp

  • Parshotam A, Hewitt AE (1993) Application of the Rothamsted carbon turnover model to soils in degraded semi-arid land in New Zealand. Environ Int 21:693–697

    Article  Google Scholar 

  • Parton WJ, Schimel DS, Cole CV, Ojima DS (1987) Analysis of factors controlling soil organic matter levels in Great Plains grasslands. Soil Sci Soc Am J 51:173–1179

    Article  Google Scholar 

  • Powlson DS, Johnston AE (1994) Long-term field experiments: their importance in understanding sustainable land use. In: Greenland DJ, Szabolcs I (eds) Chapter 22 in Soil resilience and sustainable land use. CAB International, Wallingford, pp 367–394

    Google Scholar 

  • Ross DJ, Speir TW, Tate KR, Cairns A, Meyrick KF, Pansier EA (1982) Restoration of pasture after topsoil removal effects on soil carbon and nitrogen mineralisation, microbial biomass and enzyme activities. Soil Biol Biochem 14:575–581

    Article  Google Scholar 

  • Ross DJ, Speir TW, Tate KR, Cowling JC, Watts HM (1984) Restoration of pasture after topsoil removal: changes in soil biochemical properties over a 5-year period - a note. N Z J Sci 27:419–422

    Google Scholar 

  • Schipper LA, Degens BP, Sparling GP, Duncan L (2001) Changes in microbial heterotrophic diversity along five plant successional sequences. Soil Biol Biochem 33:2093–2103

    Article  Google Scholar 

  • Schipper LA, Percival HJ, Sparling GP (2004) An approach for estimating maximum nitrogen storage in soils. Soil Use Manag 20:281–286

    Article  Google Scholar 

  • Schipper LA, Baisden WT, Parfitt RL, Ross C, Claydon JJ, Arnold G (2007) Large losses of soil C and N from soil profiles under pasture in New Zealand during the past 20 years. Glob Change Biol 13:1138–1144

    Article  Google Scholar 

  • Shepherd TG, Saggar S, Newman RH, Ross CW, Dando JL (2001) Tillage-induced changes to soil structure and organic carbon fractions in New Zealand soils. Aust J Soil Res 39:465–489

    Article  Google Scholar 

  • Soil Survey Staff (2006) Keys to soil taxonomy, 10th edn. US Department of Agriculture-NRCS, Washington, DC

  • Sparling GP, Schipper LA (2004) Soil quality monitoring in New Zealand: trends and issues arising from a broadscale survey agriculture. Ecosyst Environ 104:545–552

    Article  Google Scholar 

  • Sparling G, Parfitt RL, Hewitt AE, Schipper LA (2003a) Three approaches to define desired soil organic matter contents. J Environ Qual 32:760–766

    Article  Google Scholar 

  • Sparling G, Ross D, Trustrum N, Arnold G, West A, Speir T, Schipper L (2003b) Recovery of topsoil characteristics after landslip erosion in dry hill country of New Zealand, and a test of the space for time hypothesis. Soil Biol Biochem 35:1575–1586

    Article  Google Scholar 

  • StatSoft, Inc (2002) STATISTICA for Windows [Computer program manual]. Tulsa, OK, USA

  • Tate KR, Giltrap DJ, Claydon JJ, Newsome PF, Atkinson IAE, Taylor MD, Lee R (1997) Organic carbon stocks in New Zealand’s terrestrial ecosystems. J R Soc N Z 27:315–335

    Google Scholar 

  • Tate KR, Wilde RH, Giltrap DJ, Baisden WT, Saggar S, Trustrum NA, Scott NA, Barton JP (2005) Soil organic carbon stocks and flows in New Zealand: system development, measurement and modeling. Can J Soil Sci 85:481–489

    Article  Google Scholar 

  • Walker TW, Thapa BK, Adams AFR (1959) Studies on soil organic matter: 3. Accumulation of carbon nitrogen, sulfur, organic and total phosphorus in improved grassland soils. Soil Sci 87:135–140

    Article  Google Scholar 

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Acknowledgements

R. H. Jackman and his associates, for identifying the chronosequences of sites and collecting and publishing the original data. Marie Heaphy who patiently derived numeric data from the original graphs. M Balks (University of Waikato), P McDaniel (University of Idaho) and M McLeod (Landcare Research) provided the soil classifications. Three anonymous reviewers and Troy Baisden (Associate editor – Biogeochemistry) provided useful comments on the manuscript. GPS is a Research Associate at the University of Waikato. Part of the work was funded by Landcare Research through contract C09X0705 with the Foundation of Research, Science and Technology, and the University of Waikato.

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Schipper, L.A., Sparling, G.P. Accumulation of soil organic C and change in C:N ratio after establishment of pastures on reverted scrubland in New Zealand. Biogeochemistry 104, 49–58 (2011). https://doi.org/10.1007/s10533-009-9367-z

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  • DOI: https://doi.org/10.1007/s10533-009-9367-z

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