• 沒有找到結果。

Addiscott, T.M., Thomas, D., 2000, Tillage, mineralization and leaching: phosphate, Soil & Tillage Research 53, 255-273.

Ahmad, M., Lee, S.S., Dou, X., Mohan, D., Sung, J.K., Yang, J.E., Ok, Y.S., 2012, Effects of pyrolysis temperature on soybean stover- and peanut shell-derived biochar properties and TCE adsorption in water, Bioresource Technology 118, 536–544.

Almendros, G., Knicker, H., Francisco, J. González-Vila, 2003 , Rearrangement of carbon and nitrogen forms in peat after progressive thermal oxidation as

determined by solid-state 13C- and 15N-NMR spectroscopy, Organic Geochemistry 34, 1559-1568.

Ameloot, N., Neve, D. S., Kanagaratnam Jegajeevagan, K., Yildiz, G., Buchan, D., Funkuin, Y.N., Wolter Prins, W., Bouckaert, L., Steven Sleutel, S., Short-term CO2

and N2O emissions and microbial properties of biochar amended sandy loam soils, Soil Biology & Biochemistry 57, 401-410.

An, D., Guo, Y., Zou, B., Zhu, Y., Zichen, w., 2011, A study on the consecutive preparation of silica powders and active carbon from rice husk ash, Biomass and Bioenergy 35, 1227-1234.

Asai, H., Samson, B.K., Stephan, H.M., Songyikhangsuthor, K., Homma, K., Kiyono, Y., Inoue, Y., Shiraiwa, T., Horie, T.,2009, Biochar amendment techniques for upland rice production in Northern Laos: 1. Soil physical properties, leaf SPAD and grain yield, Field Crops Research 111, 81-84.

Asmar, F., Eiland, F., Nielsen, N.E., 1994, Effect of extracellular-enzyme activities on solubilization rate of soil organic nitrogen, Biology and Fertility of Soils 17, 32-38.

Atkinson, C. J., Fitzgerald, J.D., Hipps N.A., 2010, Potential mechanisms for achieving agricultural benefits form biochar application to temperate soils: a review, Plant and Soil 337, 1-18.

Baldock, J.A., Smernik, R.J., 2002, Chenical composition and bioavailability of thermally altered Pinus resinosa (Red pine) wood, Organic Geochemistry 33, 1093-1109.

Brady, N., and Weil, R., 2008, The Nature and Properties of Soils, 14th Edition.

Prentice Hall Inc, New Jersey, USA.

Brewer, C.E., Unger, R., Schmidt-Rohr, K., Brown, R.C., 2011, Criteria to select biochars for field studies based on biochar chemical properties, Bioenergy Research 4, 312-323.

Broaddus, G.M., York, J.E., Moseley, J.M., Factors affecting the levels of nitratel nitrogen in cured tobacco leaves, Tobacco Science 9, 149-157.

Bruun, E. W., Ambus, P., Egsgaard, H., Hauggaard-Nielsen, H., 2012, Effects of slow and fast pyrolysis biochar on soil C and N turnover dynamics, Soil Biology and Biochemistry 46, 73-79.

Chan, K. Y., Zwieyen, L. Van, Meazaros, I., Downie, A., Joseph, S., 2007,

Agronomic values of greenwaste biochar as a soil amendment, Australian Journal of Soil Research 45, 629-634.

Chan, K.Y., Van Zwieten, L., Meszaros, I., Downie, A., Joseph, S., 2008, Using poultry litter biochars as soil amendments, Australian Journal of Soil Research 46,

437-444.

Chen, B., Zhou, D., Zhu, L., 2008, Transitional adsorption and partition of nonpolar and polar aromatic contaminants by biochars of pine needles with different pyrolytic temperatures, Environmental Science & Technology 42, 5137-5143.

Chen, B., Chen, Z., 2009, Sorption of naphthalene and 1-naphthol by biochars of orange peels with different pyrolytic temperatures, Chemosphere 76, 127-133.

Cheng C.H., Lehmann, J., Thies, J.E., Burton, S.D., Engelhard, M.H., 2006, Oxidation of black carbon by biotic and abiotic processes, Organic Geochemistry 2006, 1447-1488.

Cheng, C.H., Lehmann, J., Engelhard, M.H., 2008, Natural oxidation of black carbon in soils: changes in molecular form and surface charge along a climosequence,

Geochimica et Cosmochimica Acta 72, 1598-1610.

Chun, Y., Sheng, G., Chiou, C.T., Xing, B., 2004, Composition and sorptive properties of corp residue-drived chars, Environmental Science & Technology 38,

4649-4655.

Freitas, J.C.C, Bonagamba, T.J., Emmerich, F.G., 2001, Investigation of biomass- and polymer-based carbon materials using 13C high-resolution solid-state NMR, Carbon 39, 535-545.

Gaskin, J.W., Speir, R.A., Harris, K., Das, K.C., Lee, R.D., Morris, L.A., Fisher, D.S., 2010, Effect of Peanut Hull and Pine Chip Biochar on Soil Nutrients, Corn

Nutrient Status, and Yield, Agronomy Journal 102, 623-633.

Glaser, B., Lehmann, J., Zech, W., 2002, Ameliorating physical and chemical properties of highly weathered soils in the tropics with charcoal—a review.

Biology and Fertility of Soil 35, 219–230.

Grechi, I., Vivin, P., Hilbert, G., Milin, S., Robert, T., Gaudillère, J.P., 2007, Effect of light and nitrogen supply on internal C:N balance and control of root-to-shoot biomass allocation in grapevine, Environmental and Experimental Botany 59, 139-149.

Hossain, M.K., Strezov, V., Chan, K.Y., Nelson, P.F., 2010, Agronomic properties of wastewater sludge biochar and bioavailability of metals in production of cherry tomato (Lycopersicon esculentum), Chemosphere 78, 1167–1171.

Jeffery, S., Verheijena, F.G.A., van der Veldea, M. Bastos, A.C., 2011, A quantitative review of the effects of biochar application to soils on crop productivity using meta-analysis, Agriculture, Ecosystems & Environment 144, 175–187.

Karhu, K., Mattila, T., Bergström, I., Regina, K., 2011, Biochar addition to

agricultural soil increased CH4 uptake and water holding capacity – Results from a short-term pilot field study, Agriculture, Ecosystems and Environment 140,

309–313.

Keiluweit M., Peter S., Mark G.J., Markus K. 2010, Dynamic molecular structure of plant biomass-drived black barbon (biochar), Environment Science Technology 44, 1247-1253.

Kempers, A.J., 1974, Determination of sub-microquantities of ammonium and nitrates in soils with phenol, sodiumnitroprusside and hypochlorite, Geoderma 12,

201-206.

Kloss, S., Zehetner, F., Dellantonio, A., Hamid, R., Ottner, F., Liedtke, V., Schwanninger, M., Gerzabek, M.H., Soja, G., 2012,Characterization of slow pyrolysis biochars: effects of feedstocks and pyrolysis temperature on biochar properties, Journal of Environmental Quality 41, 990-1000.

Kim, K. H., Kim, Jae-Young, Cho, Tae-Su, Choi, J.W., 2012, Influence of pyrolysis temperature on physicochemical properties of biochar obtained from the fast pyrolysis of pitch pine (Pinus rigida), Bioresource Technology 188, 158-162.

Kordatos, K., Gavela, S., Ntziouni, A., Pistiolas, K.N., Kyritsi, A.,

Kasselouri-Rigopoulou, V., Synthesis of highly siliceous ZSM-5 zeolite using silica from rice husk ash, Microporous and Mesoporous Materials 115, 189-196.

Krishnarao, R.V., Subrahmanyam, J., Kumar, T.J., 2001, Studies on the formation of black particles in rice husk silica ash, Journal of the European Ceramic Society 21, 99-104.

Kuzyakov, Y., Friedel, J.K., Stahr, K., 2000, Review of mechanisms and

quantificationof priming effects, Soil Biology & Biochemistry 32, 1485-1498.

Laird, D., Fleming, P., Wang, B., Horton, R., Karlen D., 2010, Biochar impact on nutrient leaching form a Midwestren agricultural soil, Geoderma, 158:436-442.

Lehmann, J., de Silva J.P. Jr, Steiner, C., Nehls, T., Zech, W., Glaser, B., 2003, Nutrient availability and leaching in an archaeological Anthrosol and a Ferralsol of the Central Amazon basin: fertilizer, manure and charcoal amendments., Plant and Soil 249, 343–357

Lehmann, J., Joseph S., 2009, Biochar for environmental management: science and Technology, EarthScan, London.

McBeath, A.V., Smernik, R.J., Schneider, M.P.W, Schmidt, M.W.I, Plant, E.L., 2011, Determination of the aromaticity and the degree of aromatic condensation of a thermosequence of wood charcoal using NMR, Organic Geochemistry 42, 1194-1202.

Mehlich, A., 1984. Mehlich 3 Soil Test Extractant: a modification of Mehlich 2 Extractant. Commun. Soil. Sci. Plan. 15, 1409–1416.

Mukherjee, A., Zimmerman, A.R., 2013, Organic carbon and nutrient release from a range of laboratory-produced biochars and biochar–soil mixtures, Geoderma 193–194, 122–130.

Nag, S. K., Kookana, R., Smith, L., Krull, E., Macdonald, L. M., Gill, Gurjeet, 2011, Poor efficacy of herbicides in biochar-amended soils as affected by their chemistry and mode of action, Chemosphere 84, 1572-1577.

Nguyen, T.H., Cho, H.H., Poster, D.L., Ball, W.P., 2007, Evidence for a pore-filling mechanism in the adsorption of aromatic hydrocarbons to a natural wood char, Environmental Science & Technology 41, 1212-1217.

Noguera, D., Rondón, M., Laossi, K.R., Hoyos, V., Lavelle, P., Cruz de Carvalho, M.H., Barot, S., 2010, Contrasted effect of biochar and earthworms on rice growth and resource allocation in different soils, Soil Biology and Biochemistry 42, 1017-1027.

Novak, J.M., Busscher, W.J., Watts, D.W., Laird, D.A., Ahmedna, M.A., Niandou, M.A.S., Short-term CO2 mineralization after additions of biochar and switchgrass to a Typic Kandiudult, Geoderma 154, 281-288.

Oguntunde, P.G., Abiodun, B.J., Ajayi, A.E., Van De Giesen, N., 2008, Effects of charcoal production on soil physical properties in Ghana, Journal of Plant Nutrition and Soil Science 171, 591–596.

Oguntunde, P.G., Fosu, M., Ajayi, A.E., Van De Giesen, N., 2004, Effects of charcoal production on maize yield, chemical properties and texture of soil, Biology and Fertility of Soils 39, 295–299.

Prendergast-Miller, M.T., Duvall,, M., Sohi, S.P., 2011, Localisation of nitrate in the rhizosphere of biochar-amended soils, Soil Biology and Biochemistry

43,2243-2246.

Qian, P. and Schoenau, J.J., 2002, Availability of nitrogen in solid manure amendments with different C:N ratios, Canadian Journal of Soil Sciences 82, 219-225.

Rajkovich, S., Enders, A., Hanley, K., Hyland, C., Zimmerman, A.R., Lehmann, J.,Corn growth and nitrogen nutrition after additions of biochars with varying properties to a temperate soil, Biology and Fertility of Soils 48, 271-284.

Schwanninger, M., Rodrigues, J.C., Pereira, H., Hinterstoisser, B., 2004, Effects of short-time vibratory ball milling on the shape of FT-IR spectra of wood and cellulose, Vibrational Spectroscopy 36, 23-40.

Sheng, G., Yang, Y., Huang, M., Yang, K., 2005, Influence of pH on pesticide sorption by soil containing wheat residue-derived char, Environmental Pollution 134,

457-463.

Solum, M.S., Pugmire, R.J., Jagtoyen, M., Derbyshire, F., 1995, Evolution of carbon structure in chemically actived wood, Carbon 33, 1247-1254.

Song, W., Guo, M., 2012, Quality variations of poultry litter biochar generated at different pyrolysis temperatures, Journal of Analytical and Applied Pyrolysis 94,138-145.

Spokas, K.A., Koskinen, W.C., Baker, J.M., Reiocosky, D.C., Impacts of woodchip biochar additions on greenhouse gas production and sorption/degradation of two herbicides in a Minnesota soil, Chemosphere 77, 574-581.

Tagoe, S.O., Horiuchi, T., Matsui, T., 2008, Effects of carbonized and dried chicken manures on the growth, yield, and N content of soybean, Plant Soil 306, 211-220.

Uchimiya, M., Wartelle, L.H., Lima, I.M., Klasson, K.T., 2010. Sorption of deisopropylatrazine on broiler litter biochars, Journal of Agricultural and Food Chemistry 58, 12350-12356.

Warnock, D.D., Mummey, D.L., McBride, B., Major, J., Lehmann, J., Rillig, M.C., 2010, Influences of non-herbaceous biochar on arbuscular mycorrhizal fungal abundances in roots and soils: Results from growth-chamber and field experiments, Applied Soil Ecology 46, 450–456.

Wu, W., Yang, M., Feng, Q., McGrouther, K., Wang, H., Lu, H., Chen, y., 2012, Chemical characterization of rice straw-derived biochar for soil amendment, Biomass and Bioenergy 47, 268-276.

Yanai, Y., Toyota, K., Okazaki, M., 2007, Effects of charcoal addition on N2O emissions from soil resulting from rewetting air-dried soil in short-term experiments, Soil Science and Plant Nutrition 53, 181–188.

Yang, Y., Sheng, G., 2003, Enhance pestcide sorption by soils containing particulate matter from crop residue burns, Environmental Science & Technology 37, 3635-3639.

Yang, Y., Sheng, G., Huang, M., 2006, Bioacailability of diuron in soil containing wheat-straw-derived char, Science of the Total Environment 354, 170-178.

Yao, Y., Gao, B., Zhang, M., Inyang, M., Zimmerman, A.R., 2012, Effect of biochar amendment on sorption and leaching of nitrate, ammonium, and phosphate in a sandy soil, Chemosphere 89, 1467-1471.

Yao, F.X., Arbestain, M.C., Virgel, S., Blanco, F., Arostegui, J., Maciá-Agulló, J.A., Macías, F., 2010, Simulated geochemical weathering of a mineral ash-rich biochar in a modified Soxhlet reactor, Chemosphere 80, 724-732.

Yu, X.Y., Ying, G.G., Kookana, R.S., 2006, Sorption and desorption behaviors of diuron in soils amended with charcoal, Journal of Agricultural and Food Chemistry 54, 8545-8550.

Yuan, J.H., Xu, R.K., Zhang, H., 2011, The forms of alkalis in the biochar produced from crop residues at different temperatures, Bioresource Technology 102, 3488–3497.

Zavalloni, C., Alberti, G., Biasiol, S., Vedove, G.D., Fornasier, F., Liu, J., Peressotti, A., 2011, Microbial mineralization of biochar and wheat straw mixture in soil: A short-term study, Applied Soil Ecology 50, 45–51.

Zheng W., Mingxin G., Teresa C., Douglas N. B., Nandakishore R., 2010, Sorption properties of greenwaste biochar for two triazine peaticides, Journal of Hazardous Materials 181, 121-126.

Zimmerman, A. R., 2010, Abiotic and microbial oxidation of laboratory-produced black carbon (biochar), Environmental Science & Technology 44, 1295-1301.

表 1 傅立葉轉換紅外線光譜上的吸收峰位置與其所代表的官能基 Table 1 Fourier transform infrared spectroscopy peak assignmemts.

Peaks (cm-1)

Groups Reference 3600-3200 O-H stretching Kim et al. (2012), Wu et al. (2012),

Keiluweit et al. (2010) 3070-3000 aromatic C-H stretching Kloss et al. (2011)

2980-2820 aliphatic C-H stretching Kim et al. (2012), Wu et al. (2012), Kloss et al. (2011)

1740-1700 carboxyl or carbonyl C=O stretching

Uchimiya et al. (2011), Kim et al.

(2012), Schwanninger et al. (2004) 1610-1580 aromatic C=C stretch and C=O

stretching

Kim et al. (2012), Uchimiya et al.

(2011), Kloss et al. (2011), 1500-1300 C-H stretching or asymmetric

C-O streching from carbonate

Kloss et al. (2011), Schwanninger et al. (2004)

1200-1000 C-O stretching from carbonhydrate

Kloss et al. (2011), Schwanninger et al. (2004)

1100, 800, 450

Si-O internal vibration Kordatos et al.,2008 885-750 aromatic C-H out of plane

C-O out of plane from carbonate

Kloss et al. (2011), Keiluweit et al.

(2010) 670 C-OH out-of-plane bending

mode

Schwanninger et al. (2004)

表 2 碳-13 核磁共振圖譜上的化學位移與其所代表的碳元素結構

Table 2 Peak assignments of solid-state nuclear magnetic resonance spectroscopy Chemical shift

(ppm)

Groups Reference 172 carboxyl resonances Almendros et al. (2003), Freitas et al.

(2001), Solum et al. (1995)

148 oxygenated aromatic carbon Freitas et al. (2001), Almendros et al.

(2003) 128 non-oxygenated aromatic

carbon

Freitas et al. (2001), 106 anomeric carbon in cellouse Solum et al. (1995) 89, 66 cellulose crystalline material Solum et al. (1995) 84, 63 cellulose amorphous material Solum et al. (1995) 80-70 resonances from cellouse Solum et al. (1995)

56 methoxy groups Solum et al. (1995), Almendros et al.

(2003)

30 aliphatic group McBeath et al. (2011), Freitas et al.

(2001)

22 methyl resonances Freitas et al. (2001), Solum et al.

(1995)

表 3 稻殼 (RH)、柳杉木材 (CJ) 與田菁植體 (SR) 的未炭化植體材料 (raw)、300

℃ (300) 與 500℃ (500) 生物炭的化學性質

Table 3 The chemical properties of rice husk (RH), Cryptomeria japonica woods (CJ) and Sesbania roxburghii (SR) in raw material (raw), 300℃(300) and 500℃(500) biochar. Exchangeable cations (mmol(+) kg-1)

K 14.8 11.5 18.4 9.4 9.2 11.2 47.8 95 124.4 Na 1.5 2 2 1.4 1.5 2.1 2 3.1 3.9 Ca 21.3 15.6 46.2 19.8 40.5 117.2 121.3 117.3 197.5 Mg 3.8 1.7 2.4 5.3 4.7 9.8 1.6 1.9 1.6 Total amount (mmole(+) kg-1)

K 42.3 55.5 81.7 26.9 44.9 105.5 346.3 517.7 1099.5 Na 3.6 4.4 4.7 9.2 4.7 29.4 154.5 208.7 371.5 Ca 23.6 33.3 49.0 45.5 71.2 164.2 150.1 294.9 853.8 Mg 14.8 21.6 30.8 18.6 29.9 61.9 88.1 147.7 338.3 Exchangeable cation/total amount ratio

K 0.35 0.21 0.23 0.35 0.20 0.11 0.14 0.18 0.11 Na 0.42 0.45 0.43 0.15 0.32 0.07 0.01 0.01 0.01 Ca 0.90 0.47 0.94 0.44 0.57 0.71 0.81 0.40 0.23 Mg 0.26 0.08 0.08 0.28 0.16 0.16 0.02 0.01 0.00

表 4 稻殼 (RH)、柳杉木材 (CJ) 與田菁植體 (SR) 的未炭化植體材料 (raw)、300℃ (300) 與 500℃ (500) 生物炭的碳-13 NMR 化 學位移分佈率

Table 4 Integration results of solid-state CPMAS 13C-NMR spectra for rice husk (RH), Cryptomeria japonica woods (CJ) and Sesbania roxburghii (SR) in raw material (raw), 300℃ biochar (300) and 500℃ biochar (500).

Material 0-45 45-110 110-160 160-190 190-225 Aliphatic C1 Aromatic C2 alkyl C O/N-alkyl C aromatic C carbonyl C Ketone C % %

RH-raw 5 75 15 4 2 80 15

RH-300 20 43 32 2 3 63 32

RH-500 13 7 75 1 4 19 75

CJ-raw 5 71 19 2 2 77 19

CJ-300 18% 41 35 2 4 59 35

CJ-500 15 10 69 1 4 25 69

SR-raw 15 67 10 6 2 81 10

SR-300 31 26 36 4 3 57 36

SR-500 13 8 73 2 4 21 73

1Aliphatic C was calculated by expressing as the ratio of aliphatic C (0-110 ppm) to total regions (0-225 ppm).

2Aromatic C was calculated by expressing as the ratio of aromatic C (110-160 ppm) to total regions (0-225 ppm).

表 5 在稻殼 (RH)、柳杉木材 (CJ) 與田菁植體 (SR) 的未炭化植體材料 (raw)、300℃ (300) 與 500℃ (500) 生物炭處理,以及有或 無施肥處理下,玉米作物的地上部乾重、地下部乾重、總乾重與根莖比

Table 5 Dry weight (g) of shoot biomass, root biomass and total biomass and R/S ratio of corn planted with (+F) and without (-F) fertilizer application in soil amended with rice husk (RH), Cryptomeria japonica woods (CJ) and Sesbania roxburghii (SR) in raw material (raw), 300℃

biochar (300) and 500℃ biochar (500).

Shoot biomass (g) Root biomass (g) Total biomass (g) R/S ratio (%)

treatment -F +F -F +F -F +F -F +F

Control 10.5±1.1b1, A2 11.9±3.0bc, B 2.2±0.3ab, A 1.7±0.4cd, B 12.7±0.9b, A 13.6±3.2c, B 0.21±0.04c, A 0.15±0.04bc, B RH-raw 3.4±0.2d, A 10.0±1.3d, B 1.5±0.5c, A 1.5±0.1d, A 4.9±0.7d, A 11.4±1.2d, B 0.44±0.14a, A 0.15±0.03c, B RH-300 9.3±1.0b, A 11.1±2.5c, B 1.9±0.3bc, A 2.3±1.0b, B 11.1±1.0b,A 13.4±3.0c, B 0.20±0.04c, A 0.21±0.09bc, A RH-500 10.7±1.8b, A 13.7±1.2ab, B 1.9±0.2bc, A 2.2±0.3bc, B 12.6±2.0b, A 15.8±1.5ab, B 0.18±0.02c, A 0.16±0.01a, B

CJ-raw 6.4±1.9c, A 12.8±0.6b, B 1.8±0.3bc, A 2.8±0.4a, B 8.3±2.2c, A 15.7±0.3ab, B 0.30±0.06b, A 0.22±0.04ab, B CJ-300 12.3±1.0a, A 12.8±0.7bc, A 2.2±0.5ab, A 1.7±0.3cd, B 14.4±0.6a, A 14.5±1.0bc, A 0.18±0.05c, A 0.13±0.02ab, B CJ-500 9.8±2.1b, A 12.8±0.7bc, B 1.5±0.2c, A 2.1±0.3bc, B 11.3±2.3b,A 14.9±0.8abc, B 0.16±0.02d, A 0.17±0.02a, A SR-raw 6.1±0.2c, A 12.0±0.9ab, B 1.8±0.1bc, A 2.4±0.3ab, B 7.9±0.3c, A 16.5±0.7a, B 0.30±0.01b, A 0.17±0.02ab, B SR-300 9.5±1.2b, A 11.5±0.3c, B 2.0±0.3b, A 1.5±0.2b, B 11.5±1.3b, A 12.9±0.4cd, B 0.21±0.04c, A 0.13±0.02ab, B SR-500 9.5±0.3b ,A 14.7±1.1a, B 2.5±0.1a, A 1.9±0.3bcd, B 12.0±0.4b, A 16.6±1.4a, B 0.27±0.01bc, A 0.13±0.01a, B

1The small letter shows the differences among treatments in column.

2 The capital letter shows the differences between with and without fertilizer in row.

表 6 在稻殼 (RH)、柳杉木材 (CJ) 與田菁植體 (SR) 的未炭化植體材料 (raw)、

300℃ (300) 與 500℃ (500) 生物炭處理,以及有或無施肥處理下,玉米作物的葉 片SPAD 值與土壤 pH 值

Table 6 soil pH of each plot and SPAD values of cron with (+F) and without (-F) fertilizer application in soil amended with rice husk (RH), Cryptomeria japonica woods (CJ) and Sesbania roxburghii (SR) in raw material (raw), 300℃ biochar (300) and 500

℃ biochar (500).

pH SPAD

Treatment -F +F -F +F

Control 6.0±0.1d1, A2 6.0±0.2c, A 29.5±3.6a, A 31.7±1.0bc, A RH-raw 6.3±0.1c, A 6.0±0.2c, B 13.7±1.5b, A 27.2±1.3c, B RH-300 5.9±0.1de, A 5.7±0.1cd, B 28.1±1.3a, A 31.8±1.5bc, B RH-500 5.8±0.1e, A 5.9±0.1cd, A 26.3±3.3a, A 37.8±1.6a, B

CJ-raw 5.8±0.1e, A 5.9±0cd, A 16.7±4.2b, A 35.2±0.7ab, B CJ-300 6.5±0.4bc, A 6.1±0.1c, B 26.8±1.1a, A 33.0±3.9ab, B CJ-500 6.5±0.1c, A 5.9±0.1cd, B 27.4±2.8a, A 35.6±2.2a, B SR-raw 6.7±0.2b, A 6.2±0.1bc, B 18.1±1.7b, A 35.2±1.7ab, B SR-300 6.8±0.2ab, A 6.3±0.3,b B 25.8±1.9a, A 32.9±2.5ab, B SR-500 6.9±0.2a, A 6.8±0.1a, A 24.3±2.9a, A 35.7±2.8a, B

1The small letter shows the differences among treatments in column.

2 The capital letter shows the differences between with and without fertilizer in row.

表 7 在稻殼 (RH)、柳杉木材 (CJ) 與田菁植體 (SR) 的未炭化植體材料 (raw)、

300℃ (300) 與 500℃ (500) 生物炭處理,以及不同達有龍施用量下的黑麥草存活 率 (%)

Table 7 Survival rate (%) of ryegrass seed after planting under different application rate of diuron in soil amended with rice husk (RH), Cryptomeria japonica woods (CJ) and Sesbania roxburghii (SR) in raw material (raw), 300℃ biochar (300) and 500℃

biochar (500).

Treatment Application Rate of Diuron (mg kg-1)

0.0 1.5 6.0 Control 100a1, A2 0d, B 0d, B

RH-raw 100a, A 0d, B 0d, B

RH-300 100a, A 100a, A 0d, B RH-500 100a, A 93±0.6b, B 0d, C

CJ-raw 100a, A 0d, B 0d, B

CJ-300 100a, A 100a, A 90±1b, B CJ-500 97±0.6a, A 90±1c, B 0d, C

SR-raw 100a, A 0d, B 0d, B

SR-300 97±0.6a, A 100a, A 97±0.6a, B SR-500 100a, A 100a, A 83±1.5c, B

1The small letter shows the differences among treatments in column.

2 The capital letter shows the differences between diuron application rate in row.

圖 1 淋洗試驗裝置設計圖

Fig. 1 The design of soil column leaching experiment equipment

圖 2 稻殼未炭化植體材料 (RH-raw)、300℃(RH-300)與 500℃(RH-500)生物炭的 FTIR 圖譜

Fig. 2 FTIR spectra of rice husk raw material (RH-raw), 300℃(RH-300) and 500℃

biochar (RH-500).

圖 3 柳杉未炭化植體材料 (CJ-raw)、300℃(CJ-300)與 500℃(CJ-500)生物炭的 FTIR 圖譜

Fig. 3 FTIR spectra of Cryptomeria japonica woods raw material (CJ-raw), 300℃

biochar (CJ-300) and 500℃biochar (CJ-500).

圖 4 田菁未炭化植體材料 (SR-raw)、300℃ (SR-300) 與 500℃ (SR-500) 生物 炭的FTIR 圖譜

Fig. 4 FTIR spectra of Sesbania roxburghii raw material (SR-raw), 300℃ biochar (SR-300) and 500℃biochar (SR-500).

圖 5 稻殼未炭化植體材料 (RH-raw)、300℃ (RH-300) 與 500℃ (RH-500) 生物 炭的13C-NMR 圖譜

Fig. 5 13C-NMR spectra of rice husk raw material (RH-raw), 300℃ biochar (RH-300) and 500℃ biochar (RH-500).

圖 6 柳杉未炭化植體材料 (CJ-raw)、300℃ (CJ-300) 與 500℃ (CJ-500) 生物炭 的13C-NMR 圖譜

Fig. 6 13C-NMR spectra of Cryptomeria japonica woods raw material (CJ-raw), 300

℃ biochar (CJ-300) and 500℃ biochar (CJ-500).

圖 7 田菁未炭化植體材料 (SR-raw)、300℃ (SR-300) 與 500℃ (SR-500) 生物 炭的13C-NMR 圖譜

Fig. 7 13C-NMR spectra of Sesbania roxburghii raw material (SR-raw), 300℃

biochar (SR-300) and 500℃ biochar (SR-500).

a

NO3-N Amount (mg kg-1 )

100

NO3-N Amount (mg kg-1 )

100 raw material, (b) 300℃ biochar and (c) 500℃ biochar. RH: rice husk; CJ:

Cryptomeria japonica wood; SR: Sesbania roxburghii.

a

b

c

NH4-N Amount (mg kg-1)

NH4-N Amount (mg kg-1 )

0.0

NH4-N Amount (mg kg-1 )

0.0

Cryptomeria japonica wood; SR: Sesbania roxburghii.

c

b

a

phosphate-P Amount (mg kg-1 )

phosphate-P Amount (mg kg-1)

0.0

phosphate-P Amount (mg kg-1)

0.0

Fig. 10 Cumulative amounts of phosphate-P in the leachate form soil and soil mixed with raw material (a), 300℃ biochar (b), 500℃ biochar (c). RH: rice husk; CJ:

Cryptomeria japonica wood; SR: Sesbania roxburghii.

a

b

c

 

Potassium Amount (mg kg-1 )

0

Potassium Amount (mg kg-1 )

0

Potassium Amount (mg kg-1 )

0

Fig. 11 Cumulative amounts of potassium in the leachate form soil and soil mixed with raw material (a), 300℃ biochar (b), 500℃ biochar (c). RH: rice husk; CJ:

Cryptomeria japonica wood; SR: Sesbania roxburghii.

a

b

c

 

Calcium Amount (mg kg-1 )

0

Calcium Amount (mg kg-1)

0

Calcium Amount (mg kg-1)

0

Fig. 12 Cumulative amounts of calcium in the leachate form soil and soil mixed with raw material (a), 300℃ biochar (b), 500℃ biochar (c). RH: rice husk; CJ:

Cryptomeria japonica wood; SR: Sesbania roxburghii.

c

b

a

 

Magnesium Amount (mg kg-1 )

10

Magnesium Amount (mg kg-1 )

10

Magnesium Amount (mg kg-1 )

10

Fig. 13 Cumulative amounts of magnesium in the leachate form soil and soil mixed with raw material (a), 300℃ biochar (b), 500℃ biochar (c). RH: rice husk; CJ:

Cryptomeria japonica wood; SR: Sesbania roxburghii.

a

b

c

附錄

Summary of two-way ANOVA by R for dry mass, R/S ratio, soil pH, leaf SPAD value, nutrient of leachate (NO3-N、NH4-N、phosphate-P、K、Mg、Ca), and ryegrass survival rate.

pH

K

Df Sum Sq Mean Sq F value Pr (>F) material 9 1651747 183527 315.28 < 2e-16 ***

week 1 252848 252848 434.37 < 2e-16 ***

material: week 9 58009 6445 11.07 1.07e-12 ***

Residuals 130 75674 582

Ca

Df Sum Sq Mean Sq F value Pr (>F)

material 9 86840 9649 24.88 <2e-16 ***

week 1 270528 270528 697.41 <2e-16 ***

material: week 9 6911 768 1.98 0.0466 * Residuals 130 50427 388

Mg

Df Sum Sq Mean Sq F value Pr (>F)

material 9 4589 510 12.319 5.89e-14 ***

week 1 28757 28757 694.783 < 2e-16 ***

material: week 9 990 110 2.658 0.00732 **

Residuals 130 5381 41

Survival rate

Df Sum Sq Mean Sq F value Pr (>F)

material 9 617.4 68.6 10.697 3.04e-10 ***

application rate 1 698.0 698.0 108.842 6.67e-16 ***

material:

application rate

9 240.2 26.7 4.162 0.00025 ***

Residuals 70 448.9 6.4

相關文件