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Rock phosphate combined with phosphate-solubilizing microorganisms and humic substance for reduction of plant phosphorus demands from single superphosphate

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Phosphorus (P) plays an important role in agroecosystems as a limiting nutrient for crop production because of its low soil availability and high requirements by plants at an early stage. Soluble P-fertilizer amendments contrast with low P use efficiency in weathering tropical soils. The aim of this work was to use P-solubilizing microorganisms (PSMs) and humic substance (HS) to enhance P solubility of natural rock phosphate (RP) of Araxá for partial replacement of single superphosphate (SSP). Two pot experiments were designed under greenhouse conditions. First, defined proportions of SSP and RP were combined in the following six treatments (T1, 0/100%; T2, 20/80%; T3, 40/60%; T4, 60/40%; T5, 80/20% and T6, 100/0% SSP/RP), using two different P-placement methods (broadcast and deep placement). The sub-optimal P fertilizer combination of 40% SSP + 60% RP was selected. In addition, deep placement of the P-fertilizer combination of SSP + RP produced a better plant response for all P rates. Based on the selected proportion of SSP/RP, a second assay was performed using mixed strains of bacteria and fungi (PSM, previously selected for RP solubilization) combined with humic acid (HA). We showed that PSM + HA treatment positively stimulated root and shoot weight compared with non-inoculated plants by 17 and 22%, respectively. Despite this biomass increase, no difference was observed in P concentration, indicating an increased P use efficiency. Overall, our findings suggest that the application of both PSM and HS with RP may be a suitable method for reduction of soluble P fertilizer demands without compromising plant yields.
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ActaHortic.1146.ISHS2016.DOI10.17660/ActaHortic.2016.1146.8
Proc.IIIInt.Sym.onOrganicMatterMgt.andCompostUseinHort.
Eds.:M.Cayuelaetal.
63
Rock phosphate combined with phosphate-
solubilizing microorganisms and humic substance for
reduction of plant phosphorus demands from single
superphosphate
V.B.Giro,K.Jindo,C.Vittorazzi,R.S.SdeOliveira,G.P.Conceição,L.P.CanellasandF.L.Olivares
NúcleodeDesenvolvimentodeInsumosBiológicosparaAgricultura,UniversidadeEstadualdoNorteFluminense
DarcyRibeiro,CamposdosGoytacazes,RiodeJaneiro,Brazil.
Abstract
Phosphorus(P)playsanimportantroleinagroecosystemsasalimitingnutrient
forcropproductionbecauseofitslowsoilavailabilityandhighrequirementsby
plantsatanearlystage.SolublePfertilizeramendmentscontrastwithlowPuse
efficiencyinweatheringtropicalsoils.TheaimofthisworkwastousePsolubilizing
microorganisms(PSMs)andhumicsubstance(HS)toenhancePsolubilityofnatural
rockphosphate(RP)ofAraxáforpartialreplacementofsinglesuperphosphate(SSP).
Twopotexperimentsweredesignedundergreenhouseconditions.First,defined
proportionsofSSPandRPwerecombinedinthefollowingsixtreatments(T1,
0/100%;T2,20/80%;T3,40/60%;T4,60/40%;T5,80/20%andT6,100/0%
SSP/RP),usingtwodifferentPplacementmethods(broadcastanddeepplacement).
ThesuboptimalPfertilizercombinationof40%SSP+60%RPwasselected.In
addition,deepplacementofthePfertilizercombinationofSSP+RPproduceda
betterplantresponseforallPrates.BasedontheselectedproportionofSSP/RP,a
secondassaywasperformedusingmixedstrainsofbacteriaandfungi(PSM,
previouslyselectedforRPsolubilization)combinedwithhumicacid(HA).Weshowed
thatPSM+HAtreatmentpositivelystimulatedrootandshootweightcomparedwith
noninoculatedplantsby17and22%,respectively.Despitethisbiomassincrease,no
differencewasobservedinPconcentration,indicatinganincreasedPuseefficiency.
Overall,ourfindingssuggestthattheapplicationofbothPSMandHSwithRPmaybea
suitablemethodforreductionofsolublePfertilizerdemandswithoutcompromising
plantyields.
Keywords:humicacid,biofertilizer,organicfarming,Pdeficiency,Acrisol
INTRODUCTION
Phosphorusplaysanimportantroleinagroecosystemsasalimitingnutrientforcrop
productionbecauseofitslowsoilavailabilityandhighearlyPrequirementsbyplants(Chien
et al., 2011). However, demands for soluble P‐fertilizer sources contrast with low P use,
beingmorecriticalinsesquioxide‐richsoilswithhighlevelsofactiveAlandFe.Inthiscase,
largeamountsofsolublesourcesofphosphatefertilizersareneededtoovercometheirhigh
P‐fixationcapacity,wherePisconvertedintoaformunavailableforplantuptake(Zhang et
al.,2003).
OnepossibleapproachforPsupplytocropsistoincludeintegrative management
practices that would increase soil organic matter and combine organic and inorganic P
sourceswithdifferentsolubilitytraitsinordertoobtainoptimalcropyield.IglesiasJimenez
etal.(1993)evaluatedtheeffectivenessofcompostasaPsource compared with soluble
inorganicPformsandobservedanincreaseinplanttissuePconcentrationwhentheorganic
Psourcewasused.Inthiscase,organicmatterapplicationcombinedcompetitiveadsorption
effects with net mineralization of organic P that resulted in a greater residual effect on P
supply.However,theuseoforganicsourcesisassociatedwitha relatively slow
mineralization process, non‐synchronized P availability and physiological requirement at
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theearlyphaseofplantgrowth.
Bycontrast,fullyacidulatedinorganicPfertilizers(i.e.,superphosphates)thatremain
themajorsourceofPapplicationusedbyfarmersaroundtheworld have exhibited a
negativeeconomicandecologicalimpactindifferentagricultureecosystems(Renner,2008).
Inaddition,inmostdevelopingcountries,superphosphatesarenotproducedlocally,andthe
supplytopoorfarmersisratherlimited.Thesecountriespossessdepositsofrockphosphate
(RP)thatcanbeusedfordirectapplicationinagriculture,beingconsideredasanagronomic
andeconomicallyattractivealternative(Zhangetal.,2003).
Selected P‐solubilizing microorganisms (PSM), technologically developed as
bioinoculants (Duarah et al., 2011; Nahas, 1996; Stamford et al., 2008), can be useful to
improve PR solubility. PSMs are ubiquitous inhabitants of soil,mainlyrepresentedby
bacteria and fungi groups. The biomineralization activity on RPismainlyattributedto
production of organic acid and subsequent lowering of pH, although other mechanisms
could operate, such as exopolysaccharide production (Nahas, 1996; Oliveira et al., 2009).
PSMconsortiumsofferthe advantageofmoreefficientP‐solubilizationcapacitythansingle
species,evencomparabletosolublePsources(BrazandNahas,2012).Othertechnological
approaches to increase RP solubilization involve bioreactors for confined reactions, using
differentcarbonand/ornitrogensourcestosupportmicrobialpopulationsandactivitysuch
as biochar (Mendes et al., 2014), agro‐industrial waste (VassilevandVassileva,2003)and
immobilizedcelltechnology(Vassilevetal.,2001).
TheaimofpresentworkwastoassesstheeffectofutilizationofRPasasubstitutefor
singlesuperphosphate(SSP)andthepotentialofmicroorganismsin thepresenceofhumic
acid(HA)onPsolubilizationandplantgrowth.CombinedapplicationofHAandPSMshave
been successfully used as a new biofertilizer for different crops (Canellas et al., 2013;
Canellasand Olivares,2014;Olivaresetal.,2015). It hasbeendemonstratedthatHAhasa
protectiveeffectonmicroorganisms(Martinez‐Balmorietal.,2013),andtherootexudation
profileofplantstreatedwithHAdisplayschangesintheeffluxof organicacids(Canellaset
al.,2008).
WeinitiallydefinedtheproperPratioinacombinationofSSPandRPthatcan
potentially achieve the maximum SSP dose, evaluating as well the effect of two different
typesofPlocalizationonplantgrowth.Subsequently,weevaluatedbioinoculant,formulated
with PSMs in combination with HA, as a new biological input for reduction of plant P
demandsintheformofSSP.
MATERIALSANDMETHODS
Experimentdesign1
Hybridmaizeseeds‘DKB789’wereplantedinplasticpotsfilledwith yellow Acrisol,
whichis one of the typicaltropical weathering acid soils in Brazil with low availableP, low
soilorganicmatter(SOM)content,loweffectivecation‐exchangecapacityandhighP‐fixation
capacity. The chemical characteristicsofthe Acrisol before and after 30 daysof incubation
withdolomitelimestonecanbenotedin(Table1).TheRPofAraxá (33% P2O5; particles
smallerthan0.044mmorsieveof325mesh)wasmixedhomogeneously with SSP. The
mixtureofSSP/RPwasappliedaccordingtotherecommendeddose of 0.14 g of P2O5kg‐1
Acrisol.Sixtreatmentsofthedifferentproportionrates(SSPandRP)weresetup:1)0%SSP
+100%RP;2)20%SSP+80%RP;3)40%SSP+60%RP;4)60%SSP+40%RP;5)80%SSP
+20%RP;6)100%SSP+0%RP.Inaddition,othermacronutrients(NandK)wereapplied
equally to the soil. Each different treatment was performed in four replicates with
randomized statistical design. TheeffectofthePlocationwasalsoevaluatedwith
broadcastingapplicationanddeepplacementbeyondtheseedsowing.After30daysunder
greenhouseconditions,dryweight(shootandroot),rootvolume(RV)androot:shootratio
weremeasured.Equationsofthepolynomialregressionmodeland the correlation
coefficientanalysis(R2)weremeasuredwiththeplottingprogramSIGMAPLOT,basedonthe
FtestattheP<0.05probabilitylevel.
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Table1. Chemical analysisofB‐horizon of yellow Acrisol soil beforeandafterlimingwith
dolomitelimestone.SB,Sumofbase;CEC,cation‐exchangecapacity.
C
(g kg-1) pH P
(mg dm-3)
K
(mg dm-3)
Ca2+ Mg2+ Al3+ H+Al SB CEC
(cmolc dm-3)
4.7 5.1 4 74 0.5 0.8 0.2 2.0 1.8 3.8
3.9 6.4 4 220 1.1 0.6 0.0 1.0 2.4 3.4
SB, Sum of base; CEC, cation-exchange capacity.
Experimentdesign2
Basedontheresultsoftheprevioustrial,anewpotexperimentwiththesame
experimental design was set up, emended with the sub‐optimal mixtureofPsourcesof
SSP/RP(40:60)andinoculatedornotwithPSMsincombinationor not with HA, in a
completely randomized designed with three treatments and four replicates. After 30 days
under greenhouse conditions, dry weight (shoot and root) and RV were measured. The
determinationofPconcentrationinplanttissuewasmeasuredby using a
spectrophotometerafterdigestionwithsulfuricacid.ThePSMbioinoculantwasformulated
asamicrobialconsortiumusingtwobacteriaandtwofungipreviouslyselectedforhighRP‐
solubilizationability (Table2)insolidandliquidmedium (Vermaetal.,2001),modifiedby
the introduction of Araxá RP. The bacterial inocula (strains BAC22andBAC14H)were
obtainedfromculturesthathadbeengrowninliquidDygsmediumat30°Cfor2daysat140
rpminarotatoryshaker (Baldani et al., 2014). The bacterial suspensions werecentrifuged
at2,000×g,resuspendedinsterilizedwaterandadjustedtoanopticaldensityof1.0at460
nm, which is equivalent to 108cellsmL
‐1.Thefungalinocula(strainsF5andF309)were
grownonsolidpotatodextroseagar(PDA)medium at 30°C for7days.Afterthat,10mLof
sterile water was added. The suspensions obtained werecounted inaNeubauerchamber
andadjustedto3×105sporesmL‐1.Allthemicroorganismsuspensionsweremixedatequal
volumeandappliedtogetherwiththeHA(20mgL‐1 of C)aroundthe localized Pfertilizer
mixture. The volume of the microbial consortium suspension was such that the final
substratemoisturewas50%.TheHAwasobtainedfromfiltercakesugarcanevermicompost
(Canellasetal.,2002).AllresultsarereportedasmeanswithstatisticalanalysisofFtestfor
varianceandFisher‐LCDtestattheP<0.05probabilitylevel.
Table2. CharacteristicsofthefourPSMsusedasbioinoculantinthepresentstudy.
Microorganism Strain number Taxonomy Origin
Bacterium BAC22 Serratia marcescens Vermicompost
Bacterium BAC14H Burkholderia sp. Soil (20-40 cm)
Fungus F5 Curvularia senegalensis Vermicompost
Fungus F309 Unidentified Vermicompost
RESULTSANDDISCUSSION
Experiment1
Theeffect of the differentproportionsof SSP/RP on plant growthandP locationare
showninFigure1.Asexpectedforsesquioxide‐richsoilswithhighlevelsofactiveAlandFe,
broadcastingPincreasedtheinteractionwiththeadsorptiveclaysurface,probablyreducing
Pavailabilityinthesoilsolution,andconsequentlyreducedthe growth rate response to
increaseddosesofappliedPfertilizer(Wisawapipatetal.,2009).Contrarily,deepplacement
ofthePfertilizerincreasedallbiometricparametersofthe plantresponses,comparedwith
thebroadapplication,resultinginaclearplantresponsetoincreaseddosesofSSP.
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Figure1. Shootdryweight(g),rootdryweight(g),rootvolume(cm3),androot/shootratio
ofmaizecultivar‘DKB789grownwithdifferentproportionsof SSP/RP and P
placement.
Concerning different proportions of SSP:RP, plant growth was increased in those
treatmentswithahighSSPproportion(100:00,80:20,60:40). On the contrary,alowplant
growth response was shown with a high RP proportion (0:100, 20:80), probably due to a
consequenceofinsufficientacidityinthesoilforsolubilizationandlimitedPsink,(Chienet
al.,2011).Thetreatmentof40:60(SSP:RP)producedhighrootproliferation(Figure1)with
respecttoothertreatments,eventhoughnosignificantdifferenceinshootproliferationwas
observed. Considering that root development is a key factor forimprovingsoilvolume,a
proportion of 40:60 was chosen for the next experiment aimed at minimizing the SPP
demandofplantsbyexploringthepotentialofPSMandHAcombination.
Experiment2
The impact of the combined application of PSMs and HA on plant growth was
observedinshoot(SDW)androotdryweight(RDW)(Figure2)using the 40:60 SSP/RP
combination of localized P fertilizer selected from Experiment 1. Interestingly, the
inoculationwithPSMswasonlyeffectiveinthepresenceofHA,increasingSDWandRDWby
17 and 22%, respectively, compared with treatment T1 (only P fertilizer). Enhanced
performance of plant‐growth‐promoting microorganisms in the presence of humic
substances has been reported previously, and a generation of new biological inputs for
agricultureproposed(Busatoetal., 2012;Canellasetal.,2013;CanellasandOlivares,2014;
Olivareset al., 2015). Humicsubstance not only enhancestheP availabilitybyrhizosphere
acidification(Canellasetal.,2008),butalsoinhibitsPfixationinsoilparticles,makinglabile
P forms available for more time for plant uptake and metabolic use (Erro et al., 2012).
However,higherPconcentrationwasfoundonlyinthe rootsintreatmentT3(Pfertilizer +
PSMandHA),andnodifferencewas found in shoots (Figure2) related tothe control(T1).
According to a previous report of PSM and HA application (Winarso et al., 2011), a weak
correlationofmacronutrientsinsoybeanshootswasobserved.TheapplicationofPSMalone
67
(T2) produced lower values for all parameters of plant growth measured (Figure 2). A
higherratioofroot/shootintreatmentT2reflectsthegeneral morphological changes
causedbyPdeficiencyduetopreferentialdistributiontotheroots(Wissuwaetal.,2005).In
addition,itisshouldbepointedoutthatavailabilityofothernutrientsinfluencePSMgrowth
andstimulatesPconsumption(Mendesetal.,2014).Hence,thepresenceofHA(T3)
providesfavorableconditionsformicroorganisms(Martinez‐Balmorietal.,2013).
Figure2. Shootdryweight(g),rootdryweight(g),rootvolume (cm3),root/shootratio,
shootphosphoruscontent(mgplant‐1)androotphosphoruscontent(mgplant‐1)
ofmaizecultivar‘DKB789.Means(±SE)followedbythesameletters do not
differsignificantlyaccordingtomeanseparationbyFtestatthe P<0.05
probabilitylevel.
CONCLUSIONS
ThereispotentialforthereductionofsolublePfertilizerdemandsbyapplicationofRP
incombinationwithselectedPSMsinthepresenceofHA.Thisinitiative can be improved
especiallybylocalizedPapplication,wherethesolubilizationconditionswouldbeoptimized
forplantgrowthbyamoredefinedenvironment,closetotherhizospherecompartment.
ACKNOWLEDGEMENTS
ThankstoCNPq,CAPES,FAPERJandINCTforBiologicalNitrogenFixation for the
fellowshipsandgrantsthatfundedthisresearch.
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... Among them is the design of a consortium with elite strains of bacteria and fungi and combining proper PSM bioinoculant formulation and delivery. The most relevant approach is for PSM to be combined with rock phosphates and stable OM or its fractions (i.e., HA and FA) to reduce P-adsorption and precipitation on the mineral lattice [3,7,30,70,77]. Microbial formulations combining P-solubilizing and P-mineralizing properties have been proposed in association with OM and slow-release mineral P-sources [7,11,30,77] as a suitable P-fertilizer complementary to fully acidulated inorganic P-sources. Reductions in phytoavailable P source application rates (e.g., single superphosphate, SSP) can be achieved without compromising crop productivity. ...
... The most relevant approach is for PSM to be combined with rock phosphates and stable OM or its fractions (i.e., HA and FA) to reduce P-adsorption and precipitation on the mineral lattice [3,7,30,70,77]. Microbial formulations combining P-solubilizing and P-mineralizing properties have been proposed in association with OM and slow-release mineral P-sources [7,11,30,77] as a suitable P-fertilizer complementary to fully acidulated inorganic P-sources. Reductions in phytoavailable P source application rates (e.g., single superphosphate, SSP) can be achieved without compromising crop productivity. ...
... Reductions in phytoavailable P source application rates (e.g., single superphosphate, SSP) can be achieved without compromising crop productivity. For example, Giro et al. [30] applied 60% of rock phosphate and 40% of SSP and, combined with MSP and HA, showed increased maize biomass by ~ 20% compared to plants that received the fertilizer. ...
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Plant growth-promoting bacteria (PGPB) and humic substances (HSs) are promising options for reducing the use of pesticides and mineral fertilizers. Although many studies have shown the effects of PGPB and HSs separately, little information is available on plant responses to the combined application of these biostimulants despite the great potential for the simultaneous action of these biological inputs. Thus, the objective of this review is to present an overview of scientific studies that addressed the application of PGPB and HSs to different crops. First, we discuss the effect of these biostimulants on biological nitrogen fixation, the various effects of the inoculation of beneficial bacteria combined with the application of HSs on promoting the growth of nonleguminous plants and how this combination can increase bacterial colonization of plant hosts. We also address the effect of PGPB and HSs on plant responses to abiotic stresses, in addition to discussing the role of HSs in protecting plants against pathogens. There is a lack of studies that address the role of PGPB + HSs in biocontrol. Understanding the factors involved in the promotion of plant growth through the application of PGPB and HSs can assist in the development of efficient biostimulants for agricultural management. This approach has the potential to accelerate the transition from conventional cultivation to sustainable agrosystems.
... In addition to their native P solubilizing capacity in soils, PSB can be combined to RP, as both are natural resources and their co-application has been demonstrated to improve RP agronomic efficiency [27][28][29][30]. Indeed, exploitation of microbial functional traits related to P solubilization, mainly in high P-retention agricultural soils, is paramount in order to propose microbial-based strategies enabling RP use efficiency, [31]. ...
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Background Increasing crop production to feed a growing population has driven the use of mineral fertilizers to ensure nutrients availability and fertility of agricultural soils. After nitrogen, phosphorus (P) is the second most important nutrient for plant growth and productivity. However, P availability in most agricultural soils is often limited because P strongly binds to soil particles and divalent cations forming insoluble P-complexes. Therefore, there is a constant need to sustainably improving soil P availability. This may include, among other strategies, the application of microbial resources specialized in P cycling, such as phosphate solubilizing bacteria (PSB). This P-mediating bacterial component can improve soil biological fertility and crop production, and should be integrated in well-established formulations to enhance availability and efficiency in use of P. This is of importance to P fertilization, including both organic and mineral P such as rock phosphate (RP) aiming to improve its agronomic efficiency in an integrated crop nutrition system where agronomic profitability of P and PSB can synergistically occur. Aim of Review The purpose of this review is to discuss critically the important contribution of PSB to crop P nutrition in concert with P fertilizers, with a specific focus on RP. We also highlight the need for PSB bioformulations being a sustainable approach to enhance P fertilizer use efficiency and crop production. Key Scientific Concepts of Review We first recognize the important contribution of PSB to sustain crop production, which requires a rational approach for both screening and evaluation of PSB enabling an accurate assessment of the bacterial effects both alone and in intertwined interaction with plant roots. Furthermore, we propose new research ideas about the development of microbial bioformulations based on PSB with a particular focus on strains exhibiting synergetic effects with RP.
... This enabled higher fixation of atmospheric N and solubilization of soil P compounds, resulting in higher root nutrient uptake. Similar effects were observed for the uptake of N (Canellas et al., 2013) and P in corn (Giro et al., 2016). ...
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... Combinatory use of PSB and rock phosphate (RP) that are considered to be natural resources has been successful through a number of applied research investigations that demonstrated an improved agronomic RP efficiency (Gomes et al., 2014;Abbasi et al., 2015;Giro et al., 2016;Bargaz et al., 2018). Exploitation of microbial functional traits related to P solubilization is paramount as to propose microbial-based strategies enabling increased RP use efficiency required in many high P-retention agricultural soils (Kumar, 2016). ...
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... The PL and RP interaction effects were not detected by changes in the P and N concentrations in maize diagnostic leaves (Table 1), suggesting that there was greater efficiency in fresh shoot matter production and the dry matter of leaves + stems and cobs with the application of PL+RP (Figure 1). Giro et al. (2016) reported increases in the dry matter of maize shoot and roots without, however, increasing P concentrations in both, were no differences between the treatments in the dry matter yields of the cobs. In the fall treatment applications, PL+RP increased the cob dry matter yields by 12 % compared to the C, 20 % compared to the PL, 28 % compared to the RP and 12 % compared to the PL+RP+M. ...
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The acid release of phosphates from rock phosphates (RP) and the retention of ammonium by inorganic phosphates have been studied separately in composting; however, there is a gap in the knowledge of combined application of RP with organic residues and microorganisms. The objectives were to evaluate the combined application of fresh poultry litter (PL) with RP and P-solubilizing microorganisms (M) on soil organic matter pools, microbial biomass C (MB-C) and on whole-plant silage maize and grain yields. Two field experiments tested the effects of timing of applications of PL (8 Mg ha–1), RP (4 Mg ha–1) and microorganisms on soil organic matter pools, nutritional aspects and productive components of maize crop whole-plant silage. A second experiment evaluated the effects of RP doses (0, 3, 6 and 9 Mg ha–1) with a fixed dose of PL (8 Mg ha–1) on maize grains. Application of PL+RP decreased soil organic C, while RP alone increased the humin fraction C compared to the control. The MB-C in soil with PL and PL+RP+M increased in comparison to the control and the RP. The application of PL, based on an average of fall and spring, increased leaves + stem dry matter, while in the fall on its own, the highest cob yield was observed in the combination of PL+RP, showing synergistic effects. The best ratio of poultry litter to rock phosphate combination is 2:1 in the anticipated fall application on the maize silage crop or immediate application on the maize grain crops.
... Despite this biomass increase, no difference was observed in P concentration, indicating an increased P use efficiency. The application of both PSM and HS with RP may be a suitable method for reduction of soluble P fertilizer demands without compromising plant yields [25]. Results described in the literature show a promising use of humic substances to improve the benefit of phosphorus solubilizing microorganism [26]. ...
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Background and aim: Nitrogen-fixing bacteria or diazotrophs have been isolated for many years using different formulations of N-free semi-solid media. However, the strategies used to isolate them, and the recipes of these media, are scattered through the published literature and in other sources that are more difficult to access and which are not always retrievable. Therefore, the aim of this work was to collate the various methods and recipes, and to provide a comprehensive methodological guide and their use by the scientific community working in the field of biological nitrogen fixation (BNF), particularly with non-leguminous plants.
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This study aims at elucidating the combined effects of humic compounds and phosphate-solubilizing bacteria (Pseudomonas putida) to improve characteristics of ultisol and to increase the yields of soybean conducted in a glasshouse. The humic compounds are extracted from rice-straw compost, the phosphate-solubilizing bacteria obtained from Bogor Agricultural University, and the soil (Typic paleudult) collected from Kentrong Banten, Indonesia. The results have shown that application of humic compounds combined with inoculation of phosphate-solubilizing bacteria increases pH and available P, and decreases exchangeable Al of an ultisol. The improved soil characteristic, however, does not lead to the significant differences in the uptake of macronutrients by plant.
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This review discusses and summarizes the latest reports regarding the agronomic utilization and potential environmental effects of different types of phosphate (P) fertilizers that vary in solubility. The agronomic effectiveness of P fertilizer can be influenced by the following factors: (1) water and citrate solubility; (2) chemical composition of solid water-soluble P (WSP) fertilizers; (3) fluid and solid forms of WSP fertilizers; and (4) chemical reactions of P fertilizers in soils. Non-conventional P fertilizers are compared with WSP fertilizers in terms of P use efficiency in crop production. Non-conventional P fertilizers include directly applied phosphate rock (PR), partially acidulated PR (PAPR), and compacted mixtures of PR and WSP. The potential impacts of the use of P fertilizers from both conventional (fully acidulated) and non-conventional sources are discussed in terms of (1) contamination of soils and plants with toxic heavy metals, such as cadmium (Cd), and (2) the contribution of P runoff to eutrophication. Best practices of integrated nutrient management should be implemented when applying P fertilizers to different cropping systems. The ideal management system will use appropriate sources, application rates, timing, and placement in consideration of soil properties. The goal of P fertilizer use should be to optimize crop production without causing environmental problems. KeywordsPhosphate fertilizers–Agronomic effectiveness–Cadmium–P runoff–Eutrophication
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