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Utilization of Extractable Soil Test Sulfate as an Indicator for - - PowerPoint PPT Presentation

Utilization of Extractable Soil Test Sulfate as an Indicator for Acid Producing Pyritic Sulfur David J. Lang and K. Keith Crouse Mississippi State University Thionic Fluvisols (acid sulfate soils) Worldw ide about 24 Mi. ha (~ 0.2 %) are


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Utilization of Extractable Soil Test Sulfate as an Indicator for Acid Producing Pyritic Sulfur

David J. Lang and K. Keith Crouse Mississippi State University

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Thionic Fluvisols (acid sulfate soils)

Worldw ide about 24 Mi. ha (~ 0.2 %) are found, mostly in SE Asia; often influenced by tide. Thionic Fluvisols are found in the coastal low lands of:

  • a. SE Asien (Vietnam,

Indonesia, Thailand)

  • b. W-Africa: Senegal, Gambia,

Sierra Leone

  • c. NE-coast of S-America

(Venezuela, Guyana)

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Grey reduced sulfidic materials are commonly encountered during active construction in the Fredericksburg/Stafford area of Virginia. These materials will usually acidify over time to pH less than 3.5 unless large amounts of lime are added and incorporated. http://www.landrehab.org/acid_sulfate_soils

  • Dr. Lee Daniels
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Victoria Australia Road Guidelines

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pH and Total Sulfur (S) are Initial Assessments

  • Stage A:

Preliminary Hazard Assessment

  • A pH of in situ soil or oxidised soil less than 5 indicates the presence
  • f ASS. pH < 5
  • Stage B: Detailed Soil Site Assessment
  • %S (% sulfur) if less than 0.03 %S, ASS are not present and the

proposed road construction activities can proceed w ithout restriction.

  • Pyritic Sulfur Fe2 S = 53.45 % Sulfur 0.03 %S = 0.0561% Pyrite
  • If the net acidity is 0.03 %S or greater, ASS are present.
  • (0.0561 % Pyrite)
  • Sulfur (S) and Acid Base Accounting Procedures are $$$$

https://w w w.vicroads.vic.gov.au/searchresultpage?q=acid%20sulfate%20soil

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Recommended Practice for Stabilization of Sulfate-Rich Subgrade Soils Texas _ National Cooperative Highw ay Research Program (NCHRP) National Academy Press http://nap.edu/22997 DOI 10.17226/22997

TEXAS HIGHWAY CONSTRUCTION GUIDELINES

SO4-S = 35.5 %S Multiply x 0.355 = % S

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METHODS FOR SULFATE QUANTIFICATION IN SOILS

  • These methodologies use different sulfate measurement

techniques

  • Chromatography,
  • Gravimetric (Turbidity)
  • Colorimetry
  • ICP
  • Most of the test methods are based on determining w ater

soluble sulfates in the soil.

  • Commonly Used Soil Test Extractants
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Soil Test Extraction Reagents

  • Reagents containing Sulfates cannot be utilized
  • Mehlich-1 extracting solution: 0.0125 M H 2SO4.
  • New er Mehlich’s (2 and 3) are OK
  • In the Northeast USA:
  • Extraction for Sulfate-S (Morgan’s / Modified Morgan’s) OK
  • North Central USA Soil Extractants: Bray, Olsen, Mehlich OK
  • South and Southeast
  • Mehlich developed in North Carolina
  • Lancaster Method Developed in Mississippi
  • Lancaster Reagents OK
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Inductively Coupled Plasma-Atomic Emission Spectroscopy (ICP-AES) Sulfur is determined by the Intensity of the Sulfate and Sulfide Emission at 180.7 nm

Colon at al, 2008. Sulfide and Sulfate Determination.. by ICP.. J. Anal. Atomic Spec 23:416-418

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Lignite Coal Mine, Choctaw County, MS

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https://pubs.usgs.gov/bul/0283/report.pdf Crider 1906 Geology of Mississippi

R H M S E L M A

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Introduction

  • Overburdens in the Mississippi Embayment are mined for lignite in Mississippi,

Louisiana and Texas. Similar Eocene deposits are mined for lignite in Wyoming, Montana and North Dakota.

  • There are unconsolidated sediment layers that are unoxidized gray materials and

may be suitable inclusion as final respreads (NOT APPROVED!).

  • Variable amounts of pyritic sulfur may be present in these overburdens selected

for reclamation that can be difficult to predict from visual characterizations.

  • Generally, red oxidized materials contain little pyritic S, so these are favored as

suitable topsoil substitutes (RedOX Approved as Respread)

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Introduction

  • Standard agricultural soil testing determines exchangeable potassium (K) and

phosphorus and extractable potassium (K), but neither pH nor the predicted lime requirement provides an indication of potentially oxidizable sulfur.

  • Normal agricultural soils contain 50 to 200 mg kg-1 extractable sulfate depending

upon seasonal sulfur mineralization stages and it can vary by extraction method utilized (Bray, Mehlich, Lancaster, etc).

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Sulfur Cycle is Very Complex and Dynamic

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https://dl.sciencesocieties.org/publications/books/abstracts/agronomymonogra/sulfuramissingl/25

Sulfur ↓ Emissions Success !

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SEASONAL CHANGES IN NUTRIENT AVAILABILITY FOR SULFUR-AMENDED EVERGLADES SOILS UNDER SUGARCANE Ye, Wright,and McCray. 2011 Journal of Plant Nutrition, 34:2095–2113. DOI: 10.1080/01904167.2011.618571 Muck Soil (Histosol) in Florida Releases NO3

  • , NH 4

+ and SO4

  • even w ithout Sulfur or N Added

SO4

  • and

NO3

  • at 200 to 400+ mg kg-1

Seasonal Mineralization Changes

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Lime Requirement of Agricultural Soils

Not Applicable for Reclaimed Mine Land w ith some Pyritic Sulfur

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Experiments in Mississippi w ith Reclaimed Lignite Lands

  • Early work w ith Red Gray Mixtures
  • Greenhouse Incubation
  • USDA Manure and Gypsum
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Objectives

  • Determine Potential Adverse Effects of Utilizing Gray

Unoxidized Deep Subsoil as a Plant Grow th Medium

  • Determine the Optimum Ratio of Gray to Red Soil as

Suitable Plant Grow th Substitute Material

  • Utilize Common Soil Test Extractable Sulfate as an Early

Indication of Pyritic Sulfur FeS2

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Site “B” w as a Sw eatman Silt Loam Soil Low Pyritic Sulfur 0.05% Light colored gray

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Site “A”

Site “A” w as from a Smithdale Sandy Loam Area There w as a small band of lignite “I or H” Seam Gray Material w ith 0.16% Pyritic Sulfur

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Site “A” w as from a Smithdale Sandy Loam Area w ith Medium to High Pyritic Sulfur 0.16% Gray unoxidized w as very dark gray, almost black

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Methods and Materials

  • Red and Gray Overburden Mixtures (w /w )
  • Gray Portion: 0, 25, 50, 75 and 100 %
  • 10 kg per pot
  • Overburdens w ere Analyzed for Pyritic S, Acid Base

Accounting (ABA) and Texture by Energy Labs, College Station, TX

  • Soil Fertility w as Analyzed by the Mississippi

Extension Soil Fertility Lab (Lancaster Extractant)

  • Included extractable Sulfate-S and Mn
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0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8

Gray 1A Gray 1B Gray 2 Gray 3 Gray 4

TOT_S SO4_S PYR_S ORG_S

All samples exceed the current 0.10% Pyritic S level Samples 2, 3 and 4 had a “benign” light gray color There w as no relationship betw een Total S levels and Organic matter %

OVERBURDEN

XXXX

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  • 8
  • 4

4 8 12 16 20 24 Gray 1A Gray 1B Gray 2 Gray 3 Gray 4 ABA NP PA

Four of the five samples have acceptable ABA levels Balanced by High CaCO3 Levels from Selma Chalk

ABA - 5 is the Regulatory Limit

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Methods

  • The Mississippi Soil Testing laboratory routinely utilizes the Lancaster solution to determine

agricultural fertilizer and lime recommendations.

  • It determines most of its parameters w ith an Optima 4300 DV ICP Spectrophometer including

Ca, Mg, P, K, Na, Zn, Mn and SO4-S, though Mn and SO4-S are not routinely reported.

  • Since 2005, all samples from reclamation research in Mississippi have had SO4-S and Mn

reported.

  • Samples w ith know n pyritic-S levels of 0.05 (B) to 0.16% (A) w ere found in some gray

unoxidized materials not suitable for topsoil replacement utilization.

  • These w ere mixed w ith various portions of suitable red oxidized materials w ith 0.00 %

pyritic-S and tested for extractable sulfate and incubated in the greenhouse for 12 months.

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Pearl Millet is Tolerant of Low pH and is a good indicator plant for Loblolly Pines

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Acid Base Accounting of Red and Gray Overburden

  • 2

2 4 6 8 10 12 14 16 18 ABA NP PA Red Site A Red Site B Gray Site A Gray Site B

ktonnes CaCO3 ktonne -1 soil

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Pyr yriti tic S Le Levels FeS2

0.02 0.04 0.06 0.08 0.1 0.12 0.14 0.16 Site A Site B Red Gray %

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Soil Fertility Analysis

  • All Major Nutrients (P, K, Ca, and Mg) Increase w ith

Increasing Levels of Gray Overburden

  • Pyrite Levels at Site A Exceed Acceptable

(Desirable?) Levels – Increased Potential Acidity

  • pH and Neutralization Potential at Site B Indicates

that this Overburden would be Suitable for only high pH Loving Plants

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Red Gray Mixtures w ith Pyrite in Gray at 0.05 and 0.16%

Red     Gray

1 2 3 4 5 6 7 8 9 25 50 75 100 LSD

Change in pH 12 to 24 Months in GH

SiteA 12Mos SiteA 24 Mos SiteB 12Mos SiteB 24 Mos

Site A = 0.16% Pyrite Site B = 0.05% Pyrite In only the Gray Material ; Red = 0.0% Pyrite

s.u. pH

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Red Gray Mixtures w ith Pyrite (FeS2) at 0.05 and 0.16%

200 400 600 800 1000 1200 25 50 75 100 LSD

Extractable SO4-S after 12 Months

Pyrite 0.16% Pyrite 0.05% Extractable SO4-S mg kg-1 Soil Site A Site B

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2 4 6 8 10 12 Site A Site B 25 50 75 100 5 10 15 20 25 30 35 40 Site A Site B 25 50 75 100

Greenhouse Grow th Response of Pearl Millet to Red Oxidized / Gray Unoxidized Mixtures

Grams per pot Grams per pot

August October Site A = 0.16% Pyrite Site B = 0.05% Pyrite In only the Gray Material ; Red = 0.0% Pyrite

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100 200 300 400 500 600 700 800 Site A Site B 25 50 75 100 100 200 300 400 500 600 700 Site A Site B 25 50 75 100

Manganese (Mn) Levels in Pearl Millet Grow ing in Red and Gray Mixtures w ith Low (Site B) and Moderate (Site A) Pyritic Sulfur

mg Mn kg-1 mg Mn kg-1 Site A 0.16% Pyrite Site B 0.05% Pyrite 1600 ppm 500 ppm August October Sufficient at 100 mg Mn kg-1; Toxic to pearl millet at > 500-1000 mg Mn kg-1. Toxic to w ildlife and Livestock at 2000 ppm (2000 mg kg-1 )

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Results and Discussion

  • Extractactable SO4- from site B (Moderate pyritic S) w as

500 to 1000 mg kg-1 initially and 150 to 180 mg kg-1 SO4- S from the low pyritic-S site (A).

  • Apparent pH remained high (7.2 to 7.8) at site A, but it

declined to 4.6 to 5.1 in the higher pyritic-S materials.

  • Economical utilization of routine agricultural soil testing

provides a viable initial screening tool prior to expenditure of scare resources for expensive

  • verburden testing procedures.
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Restoration of soils after strip mining of coal

 USDA is cooperating to find potential uses for animal and

industrial by-products.

January 2012 April 2012

USDA site

Soil respread Reclama- tion Work

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Sulfate Sulfur and Soluble Salts

100 200 300 400 500 600 700 SolSalts100x SulfateS Solsalts Duncan Sulfate-S: 344 Soluble Salts: 36 mg SO4-S kg-1 Soil Soluble Salts as EC dS m -1 converted to ohms x 10 -5 cm -1 by 100x

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Threshold Sensitivity of Various Crops

1 2 3 4 5 6 7 8 Field Crops Legume Crops Forage Grasses Forage Legumes Vegetables

Electrical Conductivity

ECThreshold ECMinT ECtoMinT

dS m -1

NRCS Soil Electrical Guidelines

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Conclusions

  • Site A with a Pyrite Level of 0.16% dropped in pH and Pearl Millet had

Increased Levels of Mn as Gray Portion Increased

  • Inclusion of Gray Unoxidized Overburden is Not Desirable for Suitable

Plant Growth, particularly loblolly pines

  • Utilization of Routine Soil Tests Provides the Mining Company and

Landowners Assurance of Good Reclamation

  • Soluble Salts and Extractable Test SO4-S can be Used as Initial Indicators
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If Sulfate Sulfur > 100 mg kg-1 Suspect Pyrite If Sulfate Sulfur > 100 to 300 mg kg-1 Check History OK if Sulfate Sulfur < 100 mg kg-1

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THANK YOU! Questions ??