Table 1.
Study Location | Biochar | Soils characteristics | Crop and Study method | Application rate (Mg ha−1); Biochar pH | Crop yield/growth resp. over control | Nutrient and water retention & availability | Reference | ||||
---|---|---|---|---|---|---|---|---|---|---|---|
Feedstocks | (Pyrolysis Temp, 0C) | Description | pH | ||||||||
China | Wheat straw | 350–550 | Calcareous loamy and silty clay loam | NA¶ | Maize and rice; Field | 10, 20, 40 with and without N | Corn: 7-12% yield Rice: 8-14% yield | NA¶ | (1) | ||
Wheat straw Maize straw | 300–600 400 | Upland Red soils (~Ultisols) | 6.7 | Rapeseed and potato; Field | 0, 2.5, 5, 10, 20, 30 & 40 | Rapeseed: 36% Potato: 54% yield | soil water stable aggregate soil organic carbon total N and C:N ratio | (2) | |||
Maize straw Wheat straw | 400 | Sandy loam and Calcic | NA¶ | Rice and maize; Field | 2.4 | Rice & maize: 6% yield | NA¶ | (2) | |||
Wheat straw | 350–550 | Hydroagric Stagnic Anthrosol | NA¶ | Rice; Field | 40 | 18.3% grain yield | NA¶ | (3) | |||
Pig manure compost, peanut husk & biosolids | 350–450 | Entic Hydroagric Anthrosol | NA¶ | Rice; Field | 0.45 | 13.5%, 28.1% & 31.4% grain yield | NA¶ | (4) | |||
Rice straw | NA¶ | Gleyi–Stagnic Anthrosol | NA¶ | Rice-wheat; Pot | 4.5 & 9 | 14.8 & 21.3% grain yield | (5) | ||||
Giant reed grass (Arundo donax) | 300–600 | Tropical sandy; 29.2% sand, 13.6% clay | 6.02 | Maize; Greenhouse column | 0, 1, 2, 5% (w/w) | Growth | Reduce in -N, Increase in WHC, improve in N bioavailability | (6) | |||
Japan | Chicken manure | 402–528 | Sandy: 47.5% sand, 11.7% clay | 7.0 | Brassica rapa; Field | 10 (pH = 10.5) | 90% growth | 25% mineralization of the total N. | (7) | ||
Wood-based (Japanese cedar and cypress) | 300 | Sand-dune soils | 6.9 | Rice; Field | 0, 20 & 40 (pH = 9.8) | Crop yield | 20–30% to 50–60% increase in available water content | (8) | |||
Rice husk | 350–400 | Haplic Andosols | NA¶ | Rice; Pot | 0.02, 0.2 & 2 kg m−2 | 14% straw yield | NA¶ | (9) | |||
USA New York | Maize Stover | 600 | Kendaia silt loam and Lima loam. | 7.36 | Maize; Field | 0, 1, 3, 12, and 30; + 108 kg N ha−1 (pH = 10.0) | No effects on yield | No improvement in crop N use efficiency; N uptake did not change; increased N retention | (10) | ||
Florida | Peanut hull & Brazilian pepperwood | 600 | Sandy: sand: 94%, clay: 3.0% | 5.9 | Laboratory column | 0.1 g char L−1 aqueous solution | Crop yield | Decrease in nitrate (34%), ammonium (35%) & phosphate (21%) leaching | (11) | ||
Idaho | Hardwood biochar & dairy manure co-application | 500 | Calcareous; Portnuef soil | 8.2 | Lab incubation | 0%, 1%, 2%, 10% by wt (pH = 6.8) | NA¶ | Improve in soil water content; increase in soil NO3-N | (12) | ||
Spain | Bamboo wood, Dairy manure, & mixed wood chip | NA¶ | Sandy to silty clay loam | 6.5 | Lab incubation | 2% (w/w; dry weight) | NA¶ | Consistent decrease in N2O emissions by 10–90% | (13) | ||
Olive-tree prunings | 450 | Vertisol: 22% sand, 51% clay | 8.2 | Wheat; Field | 2% by weight (pH = 6.6) | Crop yield | Increase in available N, P and C | (14) | |||
Germany | Peanut hull | NA¶ | Sandy | 6.0 | Quinua; Greenhouse | 100 and 200 char (pH = 8.1) | Crop yield | Increase in leaf N; decrease in greenhouse gas emissions; increase in WHC | (15) | ||
Maize biochar used as hydro-biochar | 600 | Loamy sand | 6.2 | Wheat; Pot | 0, 4, 12 (pH = 7.7) | Crop yield | No effect on N and Ca contents; decrease in plant tissue N | (16) | |||
Denmark | Straw | 730 | Coarse sandy | 6.5 | Barley; pot | 0, 8, 16, 32, 64 + (208 N+30 P) fertilizer | Yield: 6.0, 22, −12, −28, 10% | NUE was not prominent | (17) | ||
Australia | Willow wood | 550 | Tropical Ferralsol | acidic | Maize; Field | 0, 10, 25 + compost (co-composting) | 10–29% yield | Increase in soil N, P, OC & water content | (18) | ||
Bangladesh | Sawdust | 300–350 | “Alkaline” | 8.0 | Soybean; Pot | 20 (pH = 5.21) | 54% yield | Increase in available P | (19) | ||
Finland | Spruce chips (Picea abies) | 550–600 | Boreal loamy sand 83% sand, 2% clay | 4.65 | Wheat; Field | 0, 5, 10, 20, 30 + inorganic fertilizers | No effects on yield | Increase in soluble K & SOC; no effects on other soil nutrients (N, P); increase in plant-available water content | (20) | ||
Indonesia | Bark of Acacia mangium | 260–360 | “Acidic” soil | Maize; Field | 37 | 12% yield | NA¶ | (21) | |||
Philippines | Rice husk (Chimney charring process) | NA¶ | Anthraquic gleysols Humic nitisols | 6.55 4.3 | Rice; Field | 4.13 kg m−2 | Both (16-35%) & in yield | NA¶ | (22) |
BC, biochar; C, Carbon; Ca, calcium; CUE, cation exchange capacity; K, potassium; N, nitrogen; NUE, nitrogen use efficiency; OC, organic carbon; P, phosphorus; WHC, water-holding capacity.
NA, not available. The up arrows and down arrows represent, respectively, the increasing and decreasing responses of the parameters by biochar application.
References:
Zhang et al., 2016;
Liu et al., 2014;
Bian et al., 2014;
Qian et al., 2014;
Zhao et al., 2014;
Zheng et al., 2013;
Ishimori et al., 2017;
Kameyama et al., 2017;
Koyama and Hayashi, 2017;
Guerena et al., 2013;
Yao et al., 2012;
Ippolito et al., 2016;
Cayuela et al., 2013;
Olmo et al., 2014;
Kammann et al., 2011;
Reibe et al., 2015;
Bruun et al., 2012;
Agegnehu et al., 2016;
Mete et al., 2015;
Tammeorg et al., 2014;
Yamato et al., 2006;
Haefele et al., 2011.