Đánh giá sự thay đổi hình thái phẫu diện, tính chất hóa học đất và khả năng cung cấp dưỡng chất NPK cho lúa trên đất phèn Đồng bằng sông Cửu Long.Đánh giá sự thay đổi hình thái phẫu diện, tính chất hóa học đất và khả năng cung cấp dưỡng chất NPK cho lúa trên đất phèn Đồng bằng sông Cửu Long.Đánh giá sự thay đổi hình thái phẫu diện, tính chất hóa học đất và khả năng cung cấp dưỡng chất NPK cho lúa trên đất phèn Đồng bằng sông Cửu Long.Đánh giá sự thay đổi hình thái phẫu diện, tính chất hóa học đất và khả năng cung cấp dưỡng chất NPK cho lúa trên đất phèn Đồng bằng sông Cửu Long.Đánh giá sự thay đổi hình thái phẫu diện, tính chất hóa học đất và khả năng cung cấp dưỡng chất NPK cho lúa trên đất phèn Đồng bằng sông Cửu Long.Đánh giá sự thay đổi hình thái phẫu diện, tính chất hóa học đất và khả năng cung cấp dưỡng chất NPK cho lúa trên đất phèn Đồng bằng sông Cửu Long.
Trang 1THE MINISTRY OF EDUCATION AND
TRAINING CAN THO UNIVERSITY
SUMMARY OF THE DISSERTATION
Major: Soil Science Major Code: 62 62 01 03 TRAN VAN HUNG
EVALUATING CHANGES IN SOIL PROFILES, SOIL CHEMICAL PROPERTIES AND ABILITY
TO SUPPLY NPK NUTRIENTS FOR RICE PLANTED ON ACID SULFATE SOIL IN
MEKONG DELTA
Can Tho, 2022
Trang 2THIS DISSERTATION HAS BEEN COMPLETED AT
CAN THO UNIVERSITY
Supervisor:1 Prof Dr Ngo Ngoc Hung
2 Assos Prof Dr Tran Van Dung
The doctoral dissertation was evaluated by the Committees at the basic level.
Meeting at:
At:
Reviewer1:
Reviewer2:
The thesis could be found in:
Learning Resource Center of Can Tho University
National Library of Vietnam
Trang 3THE LIST OF PUBLISHED ARTICLES
1 Tran Van Hung, Le Van Dang,Ngo Ngoc Hung, 2017 Effect of
Phosphorus (P) blended with Dicarboxylated Acid Polymer (DCAP) onsoil available P, rice yield and P uptake in acid sulfate soil VietnamJournalofAgriculturalSciences,Vol15.N04:ISSN1859-0004.P(371- 379)
2 Tran Van Hung, Le Phuoc Toan, Tran Van Dung,Ngo Ngoc Hung,
2017 Morphological and physicochemical properties of acid sulfatesoils in Dong Thap Muoi Can Tho University Journal of Science,number of topics: Environment and Climate Change (2017) (2) ISSN1859-2333 P(1-10)
3 Tran Van Hung, Nguyen Quoc Khuong, Tran Ngoc Huu, Le Phuoc
Toàan, Nguyen Van Nghia,Ngo Ngoc Hung, 2018 Studying of
mineralnutrientsuptake(N,P,K)inricefromdryseasonandN,P,K,
Ca,MgsupplyingcapabilitiesfromacidsulfatesoilinMekongDelta Vietnamjournal of agriculture and Rural development 3+4/2018 ISSN 1859-
4581 P(62-71)
4 Tran Van Hung, Le Phuoc Toan, Tran Van Dung,Ngo Ngoc Hung,
2018.Studyingthemorphologicalandphysico-chemicalpropertiesof
acidsulfatesoilsinCuuLongdeltaafter20yearscultivation.Vietnam journal ofagriculture and Rural development number of topics: Development ofsustainable agriculture under the impact of climatechange:challengesandopportunitiesaugust–2018.ISSN1859-4581 P (125-136)
Trang 4Chapter 1: INTRODUCTION 1.1 The necessity of thestudy
The Mekong Delta has a relatively large area of acid sulfate soil(ASS), accounting about 1.6 million hectares Most of the acid sulfate soilsare grown in rice, with low pH, high iron and aluminum toxicity whichphosphorus fixation lead to difficult absorption for plants to limit factor inrice yield (Afzal et al., 2010; Paul et al., 2010; Qurban et al., 2015).Recently, a number of studies on NPK nutrients supplying to ricebasedonsitespecificnutrientmanagement(SSNM)intheMekongDelta that havebeen carried out to provide recommendations on fertilizers (Pham Sy Tan, 2005;Trinh Quang Khuong, 2005; Trinh Quang Khuong et al., 2010) At the same time,some other studies used the additive Avail@ polymer or the active ingredient(Dicarboxylic Acid Polymer- DCAP) cover on the DAP phosphate fertilizer toprotect the phosphate particle to limit by toxic iron and aluminum in low pH, calciumand magnesium at high pH soil conditions The results show that Avail phosphatefertilizer application has increasing the efficiency ofphosphorusandsomecropsyield(DunnandStevens,2008;Moosoetal., 2012).Therefore, the assessment of the change in morphology, the variabilityin the quality
of the acid sulfate soil and the ability to provide nutrients to rice on the acid sulfatesoil to beconsidered
1.2 The objective of thestudy
1.2.1 General objective
Thestudyaimedtoevaluatethechangeinsoilprofilemorphology, the properties
of acid sulfate soil and to determine NPK nutrient requirements for rice on acidsulfate soil in the MekongDelta
1.2.2 Specificobjectives
To evaluate the change in morphological profile and chemicalproperties of acid sulfate soil in the Mekong Delta after 20 years ofcultivation
TodeterminetheabilitytosupplyNPKnutrientsonriceoftypical acid sulfatesoils in the MekongDelta
To determine the efficiency of using phosphate fertilizer in the DAPmixed with Avail on rice of acid sulfate soil in the Mekong Delta
Trang 51.3 The activities of thestudy
Content 1:Determining the change in morphology and chemical
properties of acid sulfate soil in the Mekong Delta after 20 years forcultivation
Content2:DeterminingtheabilitytosupplyNPKnutrientstorice on typical
acid sulfate soils in the MekongDelta
Content 3:Determining the efficiency of phosphate fertilizer in the
DAP mixed with Avail for rice on acid sulfate soil in the Mekong Delta
1.4 The scientific and actual meaning of thethesis
1.4.1 The scientific of thethesis
The results on the thesis have provided information about the change
in morphology and soil chemistry after more than 20 years for cultivationApplyingfertilizermethodaccordingtovacantlottodeterminethe ability forsupplying nutrients N, P, K from soil and ability of rice yield by nutrients N, P and
K in each experimental site on acid sulfatesoil
Experimenting results for applying P fertilizer of DAP mixed withAvail to determine the efficiency of phosphate fertilizer on acid sulfate soil
on the Avail polymer active ingredient
This is a valuable resource for research, study and teaching
1.4.2 The actual meaning of thethesis
The results have determined the change in morphology and chemicalcharacteristics on five acid sulfate soil profiles after 20 yearscultivation.However,soilclassificationbasedondiagnostichorizonsand diagnosticproperties of FAO-WRB soil name did notchange
TheabilitytosupplynutrientsN,PandKfromthesoilforsummer- springricecropsat04experimentalsitesrepresenting 04 ecological regions of acidsulphate soil in the MekongDelta
autumnandwinter-The results of applying phosphate fertilizer on DAP mixed withAvailonlyeffectiveforricein01siteofheavilyactiveacidsulphatesoil
1.5 Subjects and scope ofresearch
1.5.1 Researchsubjects
The morphological and chemical properties of 05 typical acid sulfatesoils in the Mekong Delta include (Hong Dan - Bac Lieu; Phung
Trang 6Hiep - Hau Giang; Tan Thanh - Long An; Thanh Hoa - Long An; Tan Phuoc - Tien Giang).
Efficiency of using NPK fertilizer for rice on acid sulphate soil.Efficiency of using phosphate fertilizer in the form of DAP mixed with Avail polymer active ingredient for rice on acid sulfate soil
OM 5451 is a high yielding rice variety with a relatively short
growing time (88 - 95 days), has high tolerance to alum
1.5.2 Researchscope
+ In terms of space
Research on acid sulfate soil morphology and characteristics in
the Mekong Delta
The study has organized in parallel of four experiments in the ricefield for the ability of supply nutrients N, P, K and evaluation theeffectiveness of Avail for rice representing on four ecological regions ofacid sulfate soil in the Mekong Delta
+ In terms of time
Evaluating the changes in morphological profile and chemical
properties of acid sulfate soil in the Mekong Delta on two time periods (2015 comparing to 1992)
Surveying on the ability to supply nutrients N, P, K and theeffectivenessofDAPfertilizermixedwithactiveingredientAvailforrice crops inSummer-Autumn 2014 and Winter-Spring (2014 -2015)
1.6 New contributions of the thesis
Determining the morphological change levels on acid sulfate soil inthe Mekong Delta after more than 20 years for rice cultivation
Evaluating the change in chemical properties on five typical acidsulfate soil profiles in the Mekong Delta after more than 20 years ofcultivation
Determining the ability to provide nutrients N, P, K from the soil andthe ability of rice yield on nutrients N, P and K in the experimental sites onfour ecological regions of acid sulfate soil in the Mekong Delta
Evaluatingtheeffectivenessofphosphatefertilizersonacidsulfate soil mixedwith active ingredient Avail polymer
Trang 7Chapter 2: MATERIALS AND METHODS 2.1 Researchmaterials
Table 2.1: Location, Coordinates of soil profiles in 2015
Profil Symbol Profiles location (UTM-WGS.84)Coordinates
1 HD-BL Hong Dan district (now belongs to PhuocLong), Bac Lieu Province 0532992 1029322
2 PH-HG Phung Hiep district, Hau Giang Province 0567882 1080733
3 TT-LA Tan Thanh district, Long An Province 0613046 1175920
4 TH-LA Thanh Hoa district, Long An Province 0630916 1176116
5 TP-TG Tan Phuoc district, Tien Giang Province 0641482 1158609
Study area:ability to provide NPK nutrients and determine the
effectiveness of using DAP phosphate fertilizer mixed Avail for rice ontypical alum soil in the Mekong Delta (Table 2.2)
Table 2.1: Time of sowing and harvesting of rice in SA and WS at 04 experimental sites on acid sulfate soil in the Mekong Delta
Notes: LXQ-Long Xuyen Quadrangle; HAD-Depressed Areas of The Hau River;
CMP-Ca Mau Peninsula; PR-Plain of Reeds; (SA) Summer-Autumn; (WS) Winter-Spring
Trang 82.3 Hydrometeorology, farming system and seasonal calendar of
alum land survey area(As presented in thethesis)
2.4 Laboratory soil characteristics(As presented in thethesis)
2.5 Researchmethods
The relationship between the research contents on the alum land of the
Mekong Delta(As presented in the thesis)
2.5.1 Content 1: Methods of surveying Soil
Survey of natural elements and farming methods
Interviewing the households where the site of digging for samples onthe place, the history of land cultivation, solutions to renovate alum land.Survey of geomorphology, climate, water level/aquatic level, wild plants
Method of digging and describing morphology of profiles
Use2mtroughdrillingtore-explorethesoiltochoosethelocation representingthe digger/soil profiles The size of the soil profiles is 1.5 mlong,1.0mwideand1.5mdeep.Descriptionofthesoilontheplains,the
descriptionispreparedasthe2ndand4thFAO'sprinteddescription"Soil ProfilesDescription Guidelines" (1998; 2006) Identify and re-describe the morphology of soilprofile in 2015 and the research site in the periodof1992.UseaGPStolocatethelongitudeandlatitudeofthestudypoint
Method of collecting samples and analyzing of soil physico- chemical
Collect soil samples according to the soil layer, bring it to theprocessing laboratory to serve for analysis Based on the Handbook ofanalysis of soil, water, fertilizers, crops (Institute of Agriculturalization
of Turkey, 1998) to collect soil samples for early analysis(method ofanalysis of physical and chemical targets of soil which was described
in detail in the thesis).
Soil Classification method
UsetheFAO-WRBsoilclassificationsystem(2006)toclassifyand rename the soil foreach soilprofile
Assess the change of some characteristics of acid sulfate soil
Compare the morphological description results between two differenttimes (2015 and 1992), find similarities and differences in targets of soilmorphology Combine comparing soil characteristics to chart and evaluatethe direction of change according to the soil layers
Trang 92.5.2 Content2:MethodofdeterminingNPKdemandforriceonacid
sulfatesoil
Arrange NPK omission lot experiments
The experiment was carried out on 3 different on-farm researchhouseholdsateachtestsite(Table3.6),with3repetitionsonalotareaof 25 m2 Theformula for fertilizing 4 test sites in the NPK SA case is (80- 60-30), the
WS case is (100-60-30) Use OM 5451 for the experiment Fertilizer isfertilized at 3 times, 10, 20 and 45 days after sowing (DAS), in specificquantity (Table2.3)
Table 2.3: The amount of N, P and K applied at three times of 10, 20, 45 days after sowing the SA and WS rice crops
Day after sowingFertilizer types
Notes: (SA) Summer-Autumn; (WS) Winter-Spring
- The experimental treatments were shown in the (Table 2.5)
Table2.5:Treatmentsofthefieldexperimentinfourecologicalzonesofacid sulphatesoils Ordinal Treatments Description
Trang 10Determining the agronomic targets
Determination of agronomic targets(detailed in the thesis).
Determiningtheactualyieldistheyielddeterminedatthetimeofharvest on an area of5m2and converted to 14%humidity
Determining the amount of NPK of rice absorbed from fertilizer
Determine the protein content by the Kjeldahl distillation method.Analyze the phosphate using the color comparison method Measurepotassium(K)withanatomicabsorptionspectrometer.Calculatenutrient absorption arebased on leaf stem biomass and seeds with NPK content in the stems andriceseeds
Determining the possibility of supplying NPK from the soil
The soil's ability to provide nutrients (Dobermann and Fairhurst,
2000) is described as the ability to provide N fromINSsoil (indigenous
nitrogensupply)isthetotalamountofproteintheplantabsorbsinvacant
lotN(0N),butfertilizePandK(thewayofdeterminingPandKissimilar to determiningN)
INS=Thetotalamountofproteinabsorbedfromthestemsandriceseeds of the PK
lot;PS(indigenous phosphorus supply) = the total amount of phosphorus
absorbed from the stems and rice seeds of
theNKlot;IKS(indigenouspotassiumsupply)=thetotalamountofphosphorusabsorbed from the stems and rice seeds of theNPlot
Data processing
Using Excel software to draw charts, using SPSS software tocompare average differences and analyze variances by Duncanaudit
2.5.3 Content 3: Avail’s effectiveness assessmentmethod
Experimental treatment design for fertilizer P (DAP) mixed to Avail
The experiment of applying fertilizer P mixed with Avail was carriedout in parallel at 04 experimental stations (section 2) Theexperimentwascarriedouton3differenton-farmresearchhouseholdsof eachecological region, 03 time duplicates on a plot area of 25m2 Theformula offertilizer N and K2O in the Summer-Autumn season (80N + 30K2O) and(100N + 30K2O kg/ha) in the Winter-Spring season, usingthe variety OM
5451 as the experiment Fertilizer was applied at 3 times of 10, 20 and 45days after sowing time with specific amounts in (Table 2.6)
Trang 11Table 2.6: The amount of base fertilizer N, and K applied at three times of
10, 20, 45 days after sowing the SA and WS rice crops
Day after sowingFertilizer types
Table 2.7: Phosphorus fertilizer rates and phosphorus application blended with Avail
Ordinal Treatments Description
4 30P2O5+Avail - Application of Avail (2‰) coated on 30 kg
P 2 O 5 /ha
Note:Using2litersofAvail@ polymersolutionof 2‰concentrationcoatedfor1tonofDAP.
Evaluation of the influence of Avail on acid sulfate soils
Determining the influence of fertilizer P mixed to Avail for yieldcomposition and rice yield Determining the influence of fertilizer P mixed
to Avail for P content and absorption of rice plants
Trang 12Chapter 3: RESULT AND DISCUSSION 3.1 Changes in soil surface and its chemical characteristics on acid sulfate soil in Mekong Delta after 20 years ofuse
3.1.1 Changes in acid sulfate soilsurface
3.1.1.1 At Hong Dan-Bac Lieu (2015 compared to1992)
Accordingtotheresultofevaluatingtheacidsulfatesoilsurfaceat HD-BL,there has not been significant changes in the generating layer between the tworesearch times The soil surface is divided into 4 mainlayers,withthegeneratinglayerfromthegroundto200cmdepth(Ah/AB, Bgj1, Bj2, Cr).The active acid sulfate layer appears deeper than 50cm, and has Jarosite straw yellow dots(2.5Y 8/6-8/8) and acid sulfate producing matters above 140cm The soil name classifiedaccording to FAO-WRB is unchanged between the two research times (Sali-Endo- OrthiThionic Fluvisols) (Figure3.1)
Figure 3.1: Soil profile in Hong Dan-Bac Lieu (2015 compared to 1992)
3.1.1.2 At Phung Hiep-Hau Giang (2015 compared to1992)
TheresultcomparingtheacidsulfatesoilsurfaceatPH-HGbetweenthetwoperiods (Figure 3.2) showedthat thesoil surfacehad 4maingenerating layersand ABshifting layer (1992).Theevaluated soil surfacein2015consisted of4layers (Ah; Bgj1; Bgj2;Cr),whilein1992,itwas5layers (Ah;AB;Bgj;Cgj; Cr).AtBgj layerin2015,the depthwas30 cm,shallowerthan thatin1992,due to the 8 cmintegrationfrom ABlayertoBgj layer.Atthetworesearchtimes,the depth of theactiveacidsulfate layerdidnotchange,below50cm,withjarosite spots (2.5Y8/8) and theacidsulfategeneratingmatterspyrite,below110cmdepth.Theacidsulfate
Trang 13soil surface at PH-HG was categorized, according to FAO-WRB, as heavilyactive acid sulfate soil (Epi-Orthi Thionic Fluvisols).
Figure 3.2: Soil profile in Phung Hiep-Hau Giang (2015 compared to 1992)
3.1.1.3 At Tan Thanh-Long An (2015 compared to1992)
Thesoil surfaceatTT-LAin bothresearch timeswasdividedinto6generatinglayers.Thesoilsurfacein2015hadlayersofAp;AB;Bg;Bgj;Cgj;Cr,andAp; Ah;Bg; Bgj;Cgj;Cr in1992 (Figure 3.3).TheAhlayerin1992changedintoABlayerin2015,becausethesoillayerwasmodified via
accumulationofmineralsinsoilandchangesinthecolorofthesoilmatrix
Figure 3.3: Soil profile in Tan Thanh-Long An (2015 compared to 1992)
TheBg,BgjandCgjlayersin1992hadstronggleyification,rusted brown olivedots changed in to yellow olive ones (2.5Y 5/4; 6/8).However,in2015,withtheconservativedykesystem,thesoilhaddry
Trang 14andsubmergedalterationinthemodelof3crops/year,resultinginmore rusted dotsand diverse colors of dots (2.5YR 6/8 and 7.5YR 2.5/1) Thesoilsurfacehadtheactiveacidsulfatesoildeeperthan50cmandthelayer
containingacidsulfategeneratingmattersPypitedeeperthan120cm.The
soilclassificationaccordingtoFAO-WRBwasslightlyactiveacidsulfate soil (Endo-OrthiThionic Gleysols), which did not change its name after a period ofcultivation
3.1.1.4 At Thanh Hoa-Long An (2015 compared to1992)
The soil surface in TH-LA after the two research periods (Figure 3.4)had 6 generating layers, but the name of the layers has changed: soil profile
in 2015 with generating layer (Ah; AB; Bgj; Bg; Cr), soil profile in 1992including layers (Ah; Bg; Bgj; BC; Cr)
Figure 3.4: Soil profile in Thanh Hoa-Long An (2015 compared to 1992)
The soil surface in 2015 showed that the ground Ah layer hadrusteddotsalongtheroottube,darkyellowincolor(7.5YR6/8),because the agriculturalcultivation, the soil was usually dired and ventilated, leading to oxidization of Fe2+
betweenthetworesearchperiods,whichwasgleyicandhadJarositedots (2.5Y 8/6) atthe depth of 25-45cm Thus, the soil name did not change through time andkept as heavily active acid sulfate soil (Epi-Orthi ThionicFluvisols)
3.1.1.5 At Tan Phuoc-Tien Giang (2015 compared to1992)
20yearsofcultivationhadsomedifferences but notsignificant.Thesoil
AB;Bgj1;Bgj2;Cr),whilein1992,the
Trang 15numberof layerswas6 (Ah;AB;Bg; Bgj;Bj;Cr) Thecultivating layerAh(0-30cm)and the AB shiftinglayer (30-45cm) in1992had norusteddots, thisindicated that statusof thesoilwas wetandthe matrixwasfromdarkandslightbrown(7.5YR2/1)tobrownishgrey(10YR6/2).However,in2015,the ground layer Ah (0-35cm) had dark greymatix (Gley1 3/N),rustedreddishyellowdots(7.5YR6/8),simultaneously,the ABlayer(35-55cm)wasgrey(Gley15/N)withtheverticalclayaccumulationandrustedyellowishr
ed dots(7.5YR5/8) duemetabolismofmetaloxides
Figure 3.5: Soil profile in Tan Phuoc-Tien Giang (2015 compared to 1992)
To sum up, the assessment of soil survey results between the twoperiods (2015 compared to 1992) on 05 profiles acid sulfate soil in theMekong Delta showed that there is a small change in morphology as:background color of soil, color of rust spots, the maturity of the soil.However, the sulfuric diagnostic layer and diagnostic materials did notchange,sothesoilnamesof05acidsulfatesoiltypesintheMekongDelta classified by FAO-WRB did not change after 20 years ofcultivation
3.1.2 ChangesofchemicalpropertyofacidsulfatesoilintheMekong Delta after 20 yearscultivation
Results of soil analysis by generating layers of 5 soil profiles in2periods showed that: pHH2O(1:2.5)generating layers of 5 soil profiles intheyear(2015comparedto1992)didnotsignificantfluctuation.ThesoilpH value of thesurface layer of 5 soil profiles is low (pH<5), assessing thelevelofacidityfrommoderatetoveryacidic,andalsoadverseeffectsthe growth anddevelopment of rice (Shamshuddin et al.,2013)