ELECTRONIC SUPPLEMENTARY MATERIAL SOILS, SEC 2 • GLOBAL CHANGE, ENVIRON RISK ASSESS, SUSTAINABLE LAND USE • RESEARCH ARTICLE Release and migration of colloidal phosphorus from a typical agricultural field under long-term phosphorus fertilization in southeastern China Xinqiang Liang 1 • Yi Jin1 • Yue Zhao1 • Zhibo Wang2 • Rongqiang Yin1 • Guangming Tian1 Received: 19 August 2015 / Accepted: 15 October 2015 © Springer-Verlag Berlin Heidelberg 2015 Responsible editor: Chengrong Chen 1 2 College of Environmental and Resource Sciences, Zhejiang University, Hangzhou 310058, China Key Laboratory for Water Pollution Control and Environmental Safety, Zhejiang Province, Hangzhou 310058, China Xinqiang Liang liang410@zju.edu.cn 120 40 2012 35 30 80 25 60 20 15 40 Temperature (°C) Precipitation (mm) 100 10 20 5 0 20 40 60 0 100 80 Days after transplanting (d) 160 40 140 35 120 30 100 25 80 20 60 15 40 10 20 5 0 20 40 60 80 100 120 0 140 Days after transplanting (d) Fig. S1 Precipitation and daily average temperature in two rice seasons Temperature (C) Precipitation (mm) 2013 Oilseed rape 2012 c b 0-5 5-30 OM IP2 Rice 2012 b 0-5 c b 30-60 60-100 0.0 a a Rice 2013 d 5-30 60-100 0.9 c 1.2 0.0 b b a a a a a a a a a a 30-60 0.6 c 0-5 a a Soil total P (g/kg) Fig. S2 a a OM IP2 a a a a a 0.3 60-100 a CK IP1 d b 5-30 b a a a a a a a a 30-60 ab ab a CK IP1 c b 5-30 ab a a a a 60-100 a c a a a a 30-60 Soil depth (cm) b b 0-5 b Soil depth (cm) c Oilseed rape 2013 c 0.3 0.6 0.9 Soil total P(g/kg) 1.2 Soil total P content in 0-100 cm profile under different fertilization treatments after oilseed rape and rice seasons in 2012 and 2013. Different letters beside the columns at the same soil depth denote significant differences under four treatments (P<0.05) Table S1 Summary of reported literatures on contents and distribution colloidal P in agricultural fields Soil Fertilization Soil phosphorus Object Size distribution and Proportion type regimes content conjugation and land use a Five-year 3356 μg P dm-3 Soil 220-1200 nm 23% inorganic, 22 kg P solution (molybdate -2 -1 hm a reactive P) -3 a Five-year 3356 μg P dm Soil 220-1200 nm 46% (organic inorganic, 22 kg P solution P) hm-2 a-1 b Organic and 16.8 mmol kg-1 Soil Humic 42-57% inorganic (Oxalate-extractable solution acid-metal-phosphate (<0.45 μm P) soil suspension) -1 b Organic and 18.5 mmol kg Soil Humic 20-29% inorganic (Oxalate-extractable solution acid-metal-phosphate (<0.45 μm P) soil suspension) -1 c No fertilizers 0.39 mmol kg Soil Humic 0 (Oxalate-extractable solution acid-metal-phosphate P) d d Organic, 50×103 kg P hm-2 a-1 Inorganic, 50×10 kg P hm-2 3 92.7 μmol P (<0.45μm soil solution) 33.9 μmol P (<0.45μm soil solution) Soil solution Soil solution 25-450 nm 25-450 nm 40-58% (<0.45 μm soil solution) 40-58% (<0.45 μm soil solution) Separation method Reference Microfiltration/ Ultrafiltration Shand CA, et al., 2000 Membrane filtration/Gel filtration Membrane filtration/Gel filtration Gel filtration/Membrane filtration Hens M and Merckx R, 2001 Hens M and Merckx R, 2001 Hens M and Merckx R, 2002 e Organic, 50×103-100×103 kg P hm-2 a-1 23.8 μmol P (<0.45μm soil solution) Soil solution 25-450 nm <8% (<0.45 μm soil solution) Gel filtration/Membrane filtration f Organic and inorganic 34-145 mg kg-1 (Olsen P) Runoff 1-1000 nm Ultrafiltration f Inorganic 11-101 mg kg-1 (Olsen P) Runoff 1-1000 nm 13-22% (<1μm suspension liquid) 11-39% (<1μm suspension liquid) 37-56% (<1μm suspension liquid) 75% (soil column leachate) 28% (0-30 cm, TP in water ) >94% (>30 cm, TP in water) 1.4-19% f Inorganic 4-8 mg kg-1 (Olsen P) Runoff 1-1000 nm g - 734 mg P kg-1 Column leachate 240-2000 nm h Mineral and organic fertilizers 47-140 mg P kg-1 Soil-water extracts 10-1200 nm i Inorganic 696-1320μmol P kg-1 (0-30 cm) 10-1200 nm j Organic 933 mg kg-1 Soil column leachate Column leachate 10-1000 nm Hens M and Merckx R, 2002 Turner BL, et al., 2004 Filtration Filtration/ Ultracentrifugation de Jonge L. W., et al., 2004 Ilg K, et al., 2005 Filtration/ ultracentrifugation Siemens J, et al., 2008 25-64% Filtration/ (leachate total ultracentrifugation P) Zang L, et al., 2011 k Five-year organic, 210 kg P ha-1 1726 mg P kg-1 (0-10 cm) 1150 mg P kg-1 (10-20 cm) 553 mg P kg-1 (20-30 cm) 430 mg P kg-1 (30-40 cm) 290 mg P kg-1 (40-50 cm) 228 mg P kg-1 (50-60 cm) Soil solution 10-1000 nm 78% (0-10 cm, <1μm soil suspension) 88% (20-30 cm, <1μm soil suspension) 91% (50-60 cm, <1μm soil suspension) Filtration/ ultracentrifugation Zang L, et al., 2013 a: Peaty podzol under improved grass in northern Scotland; b: Sandy podzol for livestock farming in Belgium; c: Sandy podzol as forestland in Belgium; d: Sandy podzol as permanent grassland or arable field in Belgium; e: Sandy podzol as forestland in Belgium; f: Calcareous arable soil in semi-arid area of northwest USA; g: Sandy agricultural soil in Denmark; h: Sandy cropland soils in Northern Germany; i: Loamy sand cropland soil in Northern Germany; j: Paddy soil in Taihu basin of China; k: Paddy soil in Taihu basin of China References de Jonge LW, Kjaergaard C, Moldrup P (2004) Colloids and colloid-facilitated transport of contaminants in soils: An introduction. 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