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231224s2015 xx |||||o 00| ||eng c |
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|a 10.1080/09593330.2014.963692
|2 doi
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|a pubmed25n0805.xml
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|a (DE-627)NLM241793858
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|a (NLM)25209736
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|a DE-627
|b ger
|c DE-627
|e rakwb
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|a eng
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| 100 |
1 |
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|a Li, Ronghua
|e verfasserin
|4 aut
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| 245 |
1 |
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|a Nutrient transformation during aerobic composting of pig manure with biochar prepared at different temperatures
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1 |
|c 2015
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| 336 |
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|a Text
|b txt
|2 rdacontent
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|a ƒaComputermedien
|b c
|2 rdamedia
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| 338 |
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|a ƒa Online-Ressource
|b cr
|2 rdacarrier
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| 500 |
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|a Date Completed 05.10.2015
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|a Date Revised 16.11.2017
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|a published: Print-Electronic
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|a Citation Status MEDLINE
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|a The effects of the corn stalk charred biomass (CB) prepared at different pyrolysis temperatures as additives on nutrient transformation during aerobic composting of pig manure were investigated. The results showed that the addition of CB carbonized at different temperatures to pig manure compost significantly influenced the compost temperature, moisture, pH, electrical conductivity, organic matter degradation, total nitrogen, [Formula: see text] and NH3 variations during composting. Compared with control and adding CB charred at lower temperature treatments, the addition of CB prepared over 700°C resulted in higher pH (over 9.2) and NH3 emission and lower potherb mustard seed germination index value during the thermophilic phase. Peak temperatures of composts appeared at 7 days for control and 11 days for CB added treatments. During 90 days composting, the organic matter degradation could be increased over 14.8-29.6% after adding of CB in the compost mixture. The introduction of CB in pig manure could prolong the thermophilic phase, inhibit moisture reduce, facilitate the organic matter decomposition, reduce diethylene triamine pentaacetic acid (DTPA) extractable Zn and Cu contents in pig manure composts and increase ryegrass growth. The study indicated that the corn stalk CB prepared around 500°C was a suitable additive in pig manure composting
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|a Journal Article
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|a Research Support, Non-U.S. Gov't
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|a biochar
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|a carbonized temperature
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|a compost
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|a nutrient transformation
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|a pig manure
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|a Manure
|2 NLM
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|a Nitrogen Compounds
|2 NLM
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|a Soil
|2 NLM
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|a biochar
|2 NLM
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|a Charcoal
|2 NLM
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|a 16291-96-6
|2 NLM
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|a Copper
|2 NLM
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| 650 |
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|a 789U1901C5
|2 NLM
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| 650 |
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|a Pentetic Acid
|2 NLM
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| 650 |
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|a 7A314HQM0I
|2 NLM
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| 650 |
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|a Zinc
|2 NLM
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| 650 |
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|a J41CSQ7QDS
|2 NLM
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| 700 |
1 |
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|a Wang, Quan
|e verfasserin
|4 aut
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| 700 |
1 |
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|a Zhang, Zengqiang
|e verfasserin
|4 aut
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| 700 |
1 |
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|a Zhang, Guangjie
|e verfasserin
|4 aut
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| 700 |
1 |
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|a Li, Zhonghong
|e verfasserin
|4 aut
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| 700 |
1 |
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|a Wang, Li
|e verfasserin
|4 aut
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| 700 |
1 |
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|a Zheng, Jianzhong
|e verfasserin
|4 aut
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| 773 |
0 |
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|i Enthalten in
|t Environmental technology
|d 1998
|g 36(2015), 5-8 vom: 03. März, Seite 815-26
|w (DE-627)NLM098202545
|x 0959-3330
|7 nnns
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| 773 |
1 |
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|g volume:36
|g year:2015
|g number:5-8
|g day:03
|g month:03
|g pages:815-26
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| 856 |
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|u http://dx.doi.org/10.1080/09593330.2014.963692
|3 Volltext
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