Example of hypothetical herbicide with half-life of 2 weeks - PowerPoint PPT Presentation

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Example of hypothetical herbicide with half-life of 2 weeks

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Herbicide Behavior in Soil Pesticide Applicator Recertification Training Prepared by Alan C. York N. C. State University and Timothy L. Grey University of Georgia – PowerPoint PPT presentation

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Title: Example of hypothetical herbicide with half-life of 2 weeks


1
Herbicide Behavior in Soil Pesticide Applicator
Recertification Training Prepared by Alan C.
York N. C. State University and Timothy L.
Grey University of Georgia
1
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3
  • Why is it important to understand
  • herbicide behavior in soil?
  • That behavior can affect
  • success or failure of weed control
  • presence or absence of crop injury
  • persistence of the herbicide
  • (length of control potential for carryover)
  • environmental impact

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4
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  • What is Herbicide Adsorption?
  • Binding of herbicide to soil colloids (clay
    and
  • organic matter fraction of soil)
  • Determines herbicide availability to plants
  • Also impacts leaching, volatilization, and
  • microbial degradation

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7
Factors Affecting Herbicide Adsorption 1.
Organic matter content 2. Clay content 3.
Soil moisture 4. Chemical properties of
herbicide 5. Soil pH (affects some
herbicides, not others)
7
8
  • Factors Affecting Herbicide Adsorption
  • 1. Organic matter content
  • High capacity to adsorb herbicides
  • Higher organic matter greater herbicide
  • adsorption

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9
  • Humic Matter vs Organic Matter
  • Herbicide labels base application rates on
  • organic matter content
  • Humic matter binds herbicides
  • Humic matter is the highly degraded organic
  • fraction of soil

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10
  • Factors Affecting Herbicide Adsorption
  • 1. Organic matter content
  • High capacity to adsorb herbicides
  • Negative surfaces (ionic binding) and
  • organophillic surfaces (non-ionic binding)

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  • Factors Affecting Herbicide Adsorption
  • 1. Organic matter content
  • High capacity to adsorb herbicides
  • Negative surfaces (ionic binding) and
  • organophillic surfaces (binds non-ionic
  • herbicides)
  • Greater organic matter content
  • greater herbicide adsorption

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13
  • Humic Matter vs Organic Matter
  • Herbicide labels base application rates on
  • organic matter content
  • Humic matter binds herbicides
  • Humic matter is the highly degraded organic
  • fraction of soil
  • NCDA soil analyses include humic matter content
  • Humic matter and organic matter contents highly
  • correlated absolute values differ

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Soil series Humic matter Organic
matter ------------------ -------------------
-- Rion 0.1 1.0 Norfolk
0.3 1.2 Rains 0.6 1.9 Roanoke
2.8 3.2 Cape Fear
3.1 3.4 Portsmouth 3.2 3.8 From
Blumhorst et al., Weed Technol. 4279-283.
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Factors Affecting Herbicide Adsorption 2. Clay
content Clay is negatively charged ionic
binding with positively charged
herbicides More clay more adsorption
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  • Herbicides and Soil Adsorption
  • Clay and organic matter adsorb herbicides
  • Clay and organic matter content of soil
  • affects application rate of soil-applied
  • herbicides

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Herbicide labels break soil texture
into three major categories Categories
Textural classes Coarse sand, loamy sand,
sandy loam Medium loam, silt loam, silt, sandy
clay loam, sandy clay Fine silty clay loam,
silty clay, clay loam, clay
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Application rate recommendations for Axiom
herbicide applied PRE to corn. Organic
matter content Soil texture lt 1 1 to 3 gt
3 Coarse 4-6 oz 8-11 oz 11 oz Medium 8-11
oz 11-15 oz 15 oz Fine 15 oz 15 oz 15-19 oz
Note the rate increase
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  • Herbicides and Soil Adsorption
  • Clay and organic matter adsorb herbicides
  • Clay and organic matter content of soil
  • affects application rate of soil-applied
  • herbicides
  • Clay and organic matter content also put
  • limitations on use of some herbicides

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Application rate recommendations for Sencor
DF herbicide applied PRE to soybeans.
Organic matter content Soil texture lt 2 2
to 4 gt 4 lb
product/acre Coarse Do not use 0.50
0.67 Medium 0.50 - 0.67 0.67 - 0.83 0.83 -
1.00 Fine 0.67 - 0.83 0.83 - 1.00 1.00 - 1.06
Note the rate increase
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Lexar Preemergence Rate Recommendations
For Corn1
Lexar use rate Soil OM content
(qt/A) Less than 3 3.0 qt 3 or
greater 3.5 qt Greater than 10 Not
recommended 1 Taken from Lexar label.
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Factors Affecting Herbicide Adsorption 3. Soil
moisture Herbicides are more tightly bound to
drier soil. Due to less competition with water
for binding sites under dry conditions.
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Soil water
Soil colloid
HB
H20
HB
HB HB HB HB
H20
HB
H20
HB
H20
HB
HB
HB HB
HB
HB
H20
HB
HB
HB
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Factors Affecting Herbicide Adsorption 1.
Organic matter content 2. Clay content 3.
Soil moisture 4. Chemical properties of
herbicide 5. Soil pH (affects some
herbicides, not others)
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Sorption Coefficient, KOC Measures
the tendency for pesticide adsorption by soil.
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KOC Values Low KOC Not
tightly bound to soil. Most of the herbicide
in soil solution and available for uptake,
leaching, volatilization, microbial
degradation. High KOC Tightly bound to
soil. Most of the herbicide not available for
plant uptake, leaching, volatilization,
microbial degradation.
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Herbicide KOC Values Paraquat
(Gramoxone) 1,000,000 mL/g Glyphosate
(Roundup) 24,000 mL/g Trifluralin
(Treflan) 7,000 mL/g Alachlor
(Micro-Tech) 124 mL/g Imazaquin
(Scepter) 20 mL/g
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HB
HB
-HB
Low KOC
HB
HB
HB
-HB
-HB
High KOC
-HB
HB
-HB
-HB
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Soil pH and Herbicide Adsorption
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  • Soil pH and Herbicide Adsorption
  • Non-ionizable herbicides
  • - Have no charge regardless of soil pH
  • - No effect of soil pH on adsorption

trifluralin
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Soil pH and Herbicide Adsorption B. Cationic
herbicides - Always positively charged - Very
tightly bound to colloids - Soil pH has no
effect
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Soil pH and Herbicide Adsorption C. Basic
herbicides - Charge on molecule is pH
dependent - Neutral or positively charged,
depending upon pH - Positively charged at
lower pH greater adsorption under low soil
pH
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Soil pH and Herbicide Adsorption C. Basic
herbicides - Charge on molecule is pH
dependent - Neutral or positively charged,
depending upon pH - Positively charged at
lower pH greater adsorption under low soil
pH - At low pH, less available for plant
uptake also less available for microbial
degradation and leaching
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Herbicide Leaching Downward movement of
herbicide through soil profile by water
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Importance of Leaching 1. Provides for
activation of PRE herbicides
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Importance of Leaching 1. Provides for
activation of PRE herbicides 2. Excessive
leaching may reduce weed control
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  • Importance of Leaching
  • 1. Provides for activation of PRE
  • herbicides
  • 2. Excessive leaching may reduce
  • weed control
  • Can explain crop selectivity, or
  • lack of selectivity

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Importance of Leaching 1. Provides for
activation of PRE herbicides 2. Excessive
leaching may reduce weed control 3. Can
explain crop selectivity, or lack of 4. Can
contribute to ground water contamination
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Factors Affecting Herbicide
Leaching 1. Herbicide chemical properties a. Wate
r solubility b. Degree of adsorption c. Determin
es PLP (pesticide leaching potential)
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Pesticide Leaching Potential (PLP)
of Commonly Used Herbicides
Herbicide PLP Pendimethalin (Prowl) very
low Imazethapyr (Pursuit) low Atrazine mediu
m Prometone (Pramitol) very high From North
Carolina Agricultural Chemicals Manual, chapter
1.
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  • Factors Affecting Herbicide Leaching
  • 1. Herbicide chemical properties
  • a. Water solubility
  • b. Degree of adsorption
  • c. Determines PLP (pesticide leaching potential)
  • Soil characteristics
  • Texture and organic matter
  • i. Affect adsorption
  • ii. Affect water infiltration
  • b. Determines SLP (soil leaching potential)

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Soil Leaching Potential (SLP)
of Selected NC Soils Soil
Series SLP Cape Fear very
low Alamance medium Tarboro very
high From North Carolina Agricultural
Chemicals Manual, chapter 1.
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Ground Water Contamination Potential (GWCP) for
Selected Herbicide-Soil Combinations
SLP SLP SLP SLP SLP
PLP V. Low Low Mod High V. High
V. Low V. Low V. Low Low Low Mod
Low V. Low Low Low Mod Mod
Mod Low Low Mod Mod High
High Low Mod Mod High High
V. High Mod Mod High High V. High
From N. C. Agricultural Chemicals Manual,
Chapter 1.
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Ground Water Contamination Potential (GWCP) for
Selected Herbicide-Soil Combinations
SLP SLP SLP SLP SLP
PLP V. Low Low Mod High V. High
V. Low V. Low V. Low Low Low Mod
Low V. Low Low Low Mod Mod
Mod Low Low Mod Mod High
High Low Mod Mod High High
V. High Mod Mod High High V. High
From N. C. Agricultural Chemicals Manual,
Chapter 1.
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Ground Water Contamination Potential (GWCP) for
Selected Herbicide-Soil Combinations
SLP SLP SLP SLP SLP
PLP V. Low Low Mod High V. High
V. Low V. Low V. Low Low Low Mod
Low V. Low Low Low Mod Mod
Mod Low Low Mod Mod High
High Low Mod Mod High High
V. High Mod Mod High High V. High
From N. C. Agricultural Chemicals Manual,
Chapter 1.
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Ground Water Contamination Potential (GWCP) for
Selected Herbicide-Soil Combinations
SLP SLP SLP SLP SLP
PLP V. Low Low Mod High V. High
V. Low V. Low V. Low Low Low Mod
Low V. Low Low Low Mod Mod
Mod Low Low Mod Mod High
High Low Mod Mod High High
V. High Mod Mod High High V. High
From N. C. Agricultural Chemicals Manual,
Chapter 1.
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  • Factors Affecting Herbicide Leaching
  • 1. Herbicide chemical properties
  • a. Water solubility
  • b. Degree of adsorption
  • c. Determines PLP (pesticide leaching potential)
  • Soil characteristics
  • Texture and organic matter
  • i. Affect adsorption
  • ii. Affect water infiltration
  • b. Determines SLP (soil leaching potential)
  • 3. Volume of water flow

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Herbicide
Runoff a. Movement in surface water leaving
site herbicide dissolved or suspended in water
b. Herbicide attached to soil carried by
runoff water c. Herbicide can enter rivers and
reservoirs
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Factors Affecting Amount of Herbicide
Transported by Runoff 1. Herbicide
application rate 2. Time of first rainfall,
intensity, amount 3. Soil texture (infiltration
rate) and slope 4. Chemical properties of
herbicide a. Water solubility b. Extent of
adsorption
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Reducing Herbicide Runoff Best
Management Practices (BMPs) a. No-till (reduced
soil erosion) b. Soil tilth, residue cover
(water infiltration) c. Vegetative buffer strips
(trap runoff soil) d. Containment ponds around
nurseries
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Herbicide Volatilization Change from a
solid or liquid phase to a gaseous phase,
with subsequent dissipation into the
atmosphere
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Factors Affecting Extent of Loss by
Volatilization 1. Vapor pressure of
herbicide VP
Herbicide (mm Hg _at_ 25C x 10-7)
butylate (Sutan) 130,000
Trifluralin (Treflan)
1,100 Pendimethalin (Prowl)
94 Atrazine (AAtrex)
2.9
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  • Factors Affecting Extent of Loss by
    Volatilization
  • Vapor pressure of herbicide
  • Application method
  • PrePlant Incorporated (PPI) vs Pre-Emergent
    (PRE)

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  • Factors Affecting Extent of Loss by
    Volatilization
  • Vapor pressure of herbicide
  • Application method
  • PPI vs PRE
  • 3. Adsorption
  • Greater adsorption less volatilization

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  • Factors Affecting Extent of Loss by
    Volatilization
  • Vapor pressure of herbicide
  • Application method
  • PPI vs PRE
  • 3. Adsorption
  • Greater adsorption less volatilization
  • 4. Soil temperature
  • Greater volatilization on hotter soils

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  • Factors Affecting Extent of Loss by
    Volatilization
  • Vapor pressure of herbicide
  • Application method
  • PPI vs PRE
  • 3. Adsorption
  • Greater adsorption less volatilization
  • 4. Soil temperature
  • Greater volatilization on hotter soils
  • 5. Soil moisture content
  • Greater volatilization on wet vs. dry soil

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Herbicide Fate -- Degradation
Processes 1. Microbial degradation a. Aerobic
microorganisms (require oxygen) i. Rate of
herbicide degradation related to population
of microorganisms in soil ii. Populations and
activity affected by - Soil temp 80 to 90F
best cool soil retards microbial
degradation - Soil moisture 50 to 100 field
capacity is best dry soil retards
degradation - Soil aeration poor aeration
(and flooding) retards aerobic degradation

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Herbicide Fate -- Degradation
Processes 1. Microbial degradation b. Anaerobic
microorganisms i. Do not require oxygen
ii. Survive in flooded conditions iii. Temperatu
re affects activity
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Herbicide Fate -- Degradation
Processes 2. Chemical degradation a. Non-biologic
al, chemical reactions
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Example of Chemical Degradation
N N
N N
N N
O
R
R
N
Herbicidally active
Herbicidally inactive
Less active
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  • Chemical Degradation of Herbicides
  • a. Non-biological, chemical reactions
  • Affected by temperature more
  • rapid at higher temperatures

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  • Chemical Degradation of Herbicides
  • a. Non-biological, chemical reactions
  • Affected by temperature more
  • rapid at higher temperatures
  • c. May be affected by soil pH

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  • Herbicide Persistence
  • Length of time a herbicide remains
  • phytotoxic in soil

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  • Importance of Persistence
  • Length of weed control
  • Toxicity to following crop (carryover)

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Herbicide Dissipation Over TimeHypothetical Case
Minimum concentration necessary for weed control
Herbicide conc. ( of applied)
Maximum concentration for safe recropping
Time after application (weeks)
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  • Herbicide Persistence
  • Typically expressed as half-life (t1/2),
  • or the time it takes for 50 of the
  • herbicide to breakdown to an inactive
  • form

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Herbicide Dissipation Over TimeHypothetical
Example
t1/2 6 weeks
Herbicide conc. ( of applied)
Time after application (weeks)
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Factors Affecting Herbicide
Persistence A. Soil properties B. Climatic
conditions C. Herbicide properties
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  • Herbicide Persistence
  • Typically expressed as half-life (t1/2),
  • or the time it takes for 50 of the
  • herbicide to breakdown to an inactive
  • form
  • Half-lives can vary considerably,
  • depending upon soil and environmental
  • conditions

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Herbicide Dissipation Over TimeHypothetical
Example
Favorable Environmental conditions t1/2 2
weeks
Less favorable environmental conditions t1/2
6 weeks
Herbicide conc. ( of applied)
Time after application (weeks)
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  • Importance of Persistence
  • Length of weed control
  • Toxicity to following crop (carryover)
  • Possibly illegal residues in next crop
  • Impacts environmental fate

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