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Impact of rice-straw biochar on some selected soil properties and rice (Oryza sativa L.) grain yield

Biochar is a co-product of pyrolysis of rice straw biomass, its qualities vary according to pyrolysis conditions but it mainly contains phosphorus and potassium. The carbon (C) content in biochar is stable, so it can be applied to soils which enlarging the C sink. In the present investigation, a biochar was produced from rice straw residue, characterized and its effect on rice grain yield, pH, soil organic carbon, total N and changes in NH4+–N and NO3-–N concentrations in rice soil under intermittent wetting-drying and continuous flooding were examined. The results showed that, the rice straw-derived biochair produced was neutral in pH and the cation exchange capacity 37 cmol kg -1. Application of biochar, reduces the NH4+–N and NO3-–N concentrations in soil irrespective of moisture conditions. Such effect was more pronounced on NH4+–N and NO3-–N concentrations under flooding condition and intermittent wetting&drying condition, respectively. Increasing the rate of rice straw derived biochair application rate had significantly decreased both the NH4+–N and NO3-–N concentrations in soil. The resulted rice yield from T3 (30 g biochair per kg-1 dry soil) was the highest and significant difference compared to other treatments. The biochair application significantly enhanced the total soil N, soil organic carbon and soil pH under both flooding and wetting&drying conditions.

Biochar is a co-product of pyrolysis of rice straw biomass, its qualities vary according to pyrolysis conditions but it mainly contains phosphorus and potassium. The carbon (C) content in biochar is stable, so it can be applied to
soils which enlarging the C sink. In the present investigation, a biochar was produced from rice straw residue, characterized and its effect on rice grain yield, pH, soil organic carbon, total N and changes in NH4+–N and NO3-–N concentrations in rice soil under intermittent wetting-drying and continuous flooding were examined. The results showed that, the rice straw-derived biochair produced was neutral in pH and the cation exchange capacity 37 cmol kg -1. Application of biochar, reduces the NH4+–N and NO3-–N concentrations in soil irrespective of moisture conditions. Such effect was more pronounced on NH4+–N and NO3-–N concentrations under flooding condition and intermittent wetting&drying condition, respectively. Increasing the rate of rice straw derived biochair application rate had significantly decreased both the NH4+–N and NO3-–N concentrations in soil. The resulted rice yield from T3 (30 g biochair per kg-1 dry soil) was the highest and
significant difference compared to other treatments. The biochair application significantly enhanced the total soil N, soil organic carbon and soil pH under both flooding and wetting&drying conditions.

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availability to crops (Chan et al., 2008) <strong>and</strong> therefore<br />

high levels <str<strong>on</strong>g>of</str<strong>on</strong>g> <strong>soil</strong> organic carb<strong>on</strong> accumulati<strong>on</strong> can<br />

enhance N efficiency <strong>and</strong> increases <str<strong>on</strong>g>rice</str<strong>on</strong>g> producti<strong>on</strong><br />

Liang et al., (2006); Pan et al., (2009).<br />

Effect <str<strong>on</strong>g>of</str<strong>on</strong>g> biochair <strong>on</strong> NH4 + -N <strong>and</strong> NO3 - –N dynamics<br />

Effect <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>rice</str<strong>on</strong>g>-<str<strong>on</strong>g>straw</str<strong>on</strong>g> <str<strong>on</strong>g>biochar</str<strong>on</strong>g> <strong>on</strong> NH4 + –N (mg kg -1 )<br />

c<strong>on</strong>centrati<strong>on</strong>s <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>rice</str<strong>on</strong>g> paddy <strong>soil</strong> under different<br />

water regime is shown in Figure 1. The mineral<br />

NH4 + –N <strong>and</strong> NO3 - –N c<strong>on</strong>centrati<strong>on</strong>s was increased<br />

up to tillering stage <strong>and</strong> thereafter showed a declining<br />

trend at harvesting stage. Increases <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>biochar</str<strong>on</strong>g><br />

applicati<strong>on</strong> rate markedly decreased the NH4 + –N<br />

c<strong>on</strong>centrati<strong>on</strong>s under both flooding <strong>and</strong> intermittent<br />

wetting drying c<strong>on</strong>diti<strong>on</strong>s. Irrespective <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>biochar</str<strong>on</strong>g><br />

treatments, the NH4 + –N c<strong>on</strong>tent was significantly<br />

higher in <strong>soil</strong> under submerged c<strong>on</strong>diti<strong>on</strong> than under<br />

intermittent wetting <strong>and</strong> drying c<strong>on</strong>diti<strong>on</strong>. During the<br />

<str<strong>on</strong>g>rice</str<strong>on</strong>g> crop growth, the NH4 + –N c<strong>on</strong>centrati<strong>on</strong>s was<br />

found decreased both under submerged c<strong>on</strong>diti<strong>on</strong><br />

<strong>and</strong> intermittent wetting &drying c<strong>on</strong>diti<strong>on</strong>s. NO3 - –N<br />

c<strong>on</strong>centrati<strong>on</strong>s was also influenced by the moisture<br />

regime <strong>and</strong> <str<strong>on</strong>g>biochar</str<strong>on</strong>g> applicati<strong>on</strong> (Figure 2). NO3 - –N<br />

c<strong>on</strong>centrati<strong>on</strong>s at tillering stage <strong>and</strong> harvesting<br />

growth stages, was relatively higher in <strong>soil</strong> under<br />

intermittent wetting drying cycles than that under<br />

flooding c<strong>on</strong>diti<strong>on</strong>. The applicati<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g> biochair<br />

resulted in significant decrease in NO3 - –N<br />

c<strong>on</strong>centrati<strong>on</strong>s under the two water regimes;<br />

however, the reducti<strong>on</strong> was greater at higher level <str<strong>on</strong>g>of</str<strong>on</strong>g><br />

<str<strong>on</strong>g>biochar</str<strong>on</strong>g> (T3) treatment. This effect was more<br />

pr<strong>on</strong>ounced under flooding c<strong>on</strong>diti<strong>on</strong> than the<br />

intermittent wetting <strong>and</strong> drying c<strong>on</strong>diti<strong>on</strong>. The<br />

reducti<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g> NO3 - –N c<strong>on</strong>centrati<strong>on</strong> could be<br />

attributed to <str<strong>on</strong>g>rice</str<strong>on</strong>g> uptake. As the chemistry <str<strong>on</strong>g>of</str<strong>on</strong>g> flooding<br />

<strong>soil</strong> differs from that <str<strong>on</strong>g>of</str<strong>on</strong>g> upl<strong>and</strong>, the N dynamics also<br />

changed accordingly. The submerged <strong>soil</strong> appears to<br />

be an ideal medium for both aerobic <strong>and</strong> anaerobic N<br />

fixati<strong>on</strong>, especially in the presence <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>rice</str<strong>on</strong>g> plants.<br />

Nitrogen occurs in <str<strong>on</strong>g>rice</str<strong>on</strong>g> <strong>soil</strong> as organic-N, NH4 + ,<br />

molecular N2, NO3 - <strong>and</strong> NO2. The transformati<strong>on</strong> that<br />

they undergo is largely microbial introversi<strong>on</strong>s<br />

regulated by the <strong>soil</strong> physical <strong>and</strong> chemical<br />

characterizati<strong>on</strong> Sahrawat (2005). In flooding <strong>soil</strong>,<br />

the main transformati<strong>on</strong>s are the accumulati<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g><br />

NH4 + –N, de-nitrificati<strong>on</strong> <strong>and</strong> N fixati<strong>on</strong>, depending<br />

up<strong>on</strong> nature <strong>and</strong> c<strong>on</strong>tent <str<strong>on</strong>g>of</str<strong>on</strong>g> OM, Eh, pH <strong>and</strong> <strong>soil</strong><br />

temperature. The mineralizati<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g> organic N in<br />

flooding <strong>soil</strong> stops at the NH4 + stage because <str<strong>on</strong>g>of</str<strong>on</strong>g> the<br />

lack <str<strong>on</strong>g>of</str<strong>on</strong>g> oxygen to carry the process via NO2 to NO3.<br />

Therefore, NH4 + –N accelerates under flooding<br />

c<strong>on</strong>diti<strong>on</strong>s. Whereas, in <strong>soil</strong> under intermittent<br />

wetting&drying cycles, aerati<strong>on</strong> causes active<br />

nitrificati<strong>on</strong> to take place, resulting in more NO3 - –N<br />

accumulati<strong>on</strong> Gh<strong>on</strong>eim et al., (2012). The additi<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g><br />

<str<strong>on</strong>g>biochar</str<strong>on</strong>g> to <strong>soil</strong> significantly reduces the<br />

c<strong>on</strong>centrati<strong>on</strong>s <str<strong>on</strong>g>of</str<strong>on</strong>g> <strong>soil</strong> NH4 + –N <strong>and</strong> NO3 - –N, mainly<br />

due to electrostatic adsorpti<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g> nutrients <strong>on</strong> <str<strong>on</strong>g>biochar</str<strong>on</strong>g><br />

particles. In additi<strong>on</strong>, <str<strong>on</strong>g>biochar</str<strong>on</strong>g> was can adsorb large<br />

amounts <str<strong>on</strong>g>of</str<strong>on</strong>g> NH4 + which may have lowered the NH4 + –<br />

N c<strong>on</strong>centrati<strong>on</strong>s in <strong>soil</strong> (Steiner et al., 2007).<br />

However, it should be noted that immobilizati<strong>on</strong><br />

potential associated with <str<strong>on</strong>g>biochar</str<strong>on</strong>g> additi<strong>on</strong>s to <strong>soil</strong><br />

would be greatly limited by the recalcitrant nature <str<strong>on</strong>g>of</str<strong>on</strong>g><br />

<str<strong>on</strong>g>biochar</str<strong>on</strong>g> (DeLuca <strong>and</strong> Aplet, 2007). The reducti<strong>on</strong> in N<br />

availability could be due to greater immobilizati<strong>on</strong> in<br />

<str<strong>on</strong>g>biochar</str<strong>on</strong>g> amended <strong>soil</strong> since the <str<strong>on</strong>g>biochar</str<strong>on</strong>g> used in the<br />

experiment had a high C/N ratio. Biochar applicati<strong>on</strong><br />

to agricultural <strong>soil</strong>s <str<strong>on</strong>g>of</str<strong>on</strong>g> tropics has been reported to<br />

either reduce N availability (Lehmann et al., 2003,<br />

2006) or increases N uptake (Steiner et al., 2007).<br />

Gh<strong>on</strong>eim <strong>and</strong> Ebid Page 19

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