Results of factor analysis: grouping of fatty acids derived from factor loadings and PLFA literature.G+1 and G+2 are gram positive group one and two, respectively; G-1 and G-2 are gram-negative group one and two, respectively; VAM -vesicular arbuscular mycorrhiza fungi, Ac -actinomycetes.
Security in rice production requires solving challenges of water scarcity and phosphorus (P) limitations. Reductive dissolution of ferric (III) iron bound phosphate (Fe–P) and organic P (Porg) mineralization are two understudied P sources for rice plants and microorganisms. Using the new water-saving alternate wetting-drying irrigation should increase Porg mineralization but decrease the Fe–P dissolution and thereby shift the plant and microbial preferences for P sources. Rice biomass increased two-fold under alternate wetting-drying compared to continuous flooding, but the P use efficiency of plants was independent of water regimes. Plants were more competitive for P from Fe–P by Fe(III) reduction, whereas microorganisms preferred straw-derived P (enzymatic hydrolyzation). The high contribution (∼20 %) of P from straw to the P nutrition of rice plants and microorganisms raises the significance of Porg mineralization, e.g. from organic fertilizers. This makes the application of organic P fertilizers highly beneficial to increase rice productivity. Plants took up 62 % more soil-derived P under alternate wetting-drying than under continuous flooding. Accordingly, alternate wetting-drying is a more efficient management to increase the use of soil legacy P and reduce the use of mineral fertilizers compared to continuous flooding.
The application of biochar (BC) in conjunction with mineral fertilizers is one of the most promising management practices recommended to improve soil quality. However, the interactive mechanisms of BC and mineral fertilizer addition affecting microbial communities and functions associated with soil organic matter (SOM) cycling are poorly understood. We investigated the SOM in physical and chemical fractions, microbial community structure (using phospholipid fatty acid analysis, PLFA) and functions (by analyzing enzymes involved in C and N cycling and Biolog) in a 6-year field experiment with BC and NPK amendment. BC application increased total soil C and particulate organic C for 47.4–50.4% and 63.7–74.6%, respectively. The effects of BC on the microbial community and C-cycling enzymes were dependent on fertilization. Addition of BC alone did not change the microbial community compared with the control, but altered the microbial community structure in conjunction with NPK fertilization. SOM fractions accounted for 55% of the variance in the PLFA-related microbial community structure. The particulate organic N explained the largest variation in the microbial community structure. Microbial metabolic activity strongly increased after BC addition, particularly the utilization of amino acids and amines due to an increase in the activity of proteolytic (l-leucine aminopeptidase) enzymes. These results indicate that microorganisms start to mine N from the SOM to compensate for high C:N ratios after BC application, which consequently accelerate cycling of stable N. Concluding, BC in combination with NPK fertilizer application strongly affected microbial community composition and functions, which consequently influenced SOM cycling.
Several names are used for materials produced by pyrolysis such as pyrogenic carbon, black carbon, char(coal), biochar, pyrochar or plant char (Schmidt and Noack 2000, Glaser et al. 2002, Lehmann 2007, Bird and Ascough 2011, Knicker 2011). There are two major problems related to this variety of names. First, material derived from pyrolysis is not a defi ned substance, instead material properties depend on the production process, temperature and duration which is better expressed by a combustion continuum or by elemental ratios such as O/C and H/C (Fig. 1). There is still no common defi nition for this type of materials. Second, pyrolysis products are important across a range of disciplines such as material science, natural sciences including soil science, chemistry and biology, and agronomy each of which has an own terminology and a set of methodologies for the analysis of this material and interpretation of results. The term biochar was fi rst used by Karaosmanoglu et al. (2000) for pyrogenic carbon produced on purpose by humans under controlled pyrolysis conditions in order to generate (i) gases for power generation (syngas), (ii) a range of bio-oils and (iii) biochar for soil amelioration in agriculture and for carbon sequestration.
A general strategy in modern agriculture to reduce phosphorus (P) fertilization is to rely on microbial efficiency of P acquisition and recycling from organic sources. However, this involves extracellular enzymes that require energy from ATP, so the process depends on the microbes’ physiological state and soil P availability. To elucidate the key relationships we compared P acquisition processes in P-poor soil (Cambisol) and links between C:P stoichiometry, enzyme activity, and ATP with microbial communities in contrasting activity states (dormancy, growth followed by starvation and gradually activated, respectively induced by no, single large (50 μg C g−1 soil) and multiple low (five days of 10 μg C g−1 soil day−1) additions of glucose as a carbon (C) source). A sole P input, without C addition, almost doubled microbial C (Cmic) contents, maintained stable phosphatase activity at 36 nmol h−1 per nmol ATP and raised microbial P (Pmic) 2.7-fold. In contrast, sole glucose addition increased Pmic by only 8%, confirming that P-limitation was much stronger than C limitation. Only 5–10 % of P potentially mineralized by phosphatase was recovered as microbial P. Cmic:Pmic ratios in microbial biomass <200 and >350 respectively reflected C starvation and strong P starvation. The ATP was a suitable predictor of microbial biomass in soil lacking fresh substrate, but weak predictor of microbial biomass after substrate input. Structural equation models revealed contrasting strategies of P utilization depending on microbial activity state. Dormant microorganisms (without glucose addition) invested most P to ATP production. In contrast, following substrate addition P-limited microorganisms accelerated phosphatase production, and hence capacity to mine P in organic sources. Thus, the P utilization/acquisition strategies depended on C accessibility and were modulated by P availability.