Emissions Trading to Reduce Greenhouse Gas Emissions in the United States
Methods to Reduce Fumigant Emissions
Transcript of Methods to Reduce Fumigant Emissions
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Soil Fumigants and application methods
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Conventional Soil Fumigation (Acres, California 2007):
Methyl Bromide/Chloropicrin: 40,000 Telone/Chloropicrin: 17,000 Telone II: 37,000 Chloropicrin alone: 6,000 Metam sodium: 77,000
TOTAL: ~ 180,000 acres annually
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Strawberry: Verticillium wilt • Pathogen is
Verticillium dahliae
• Survives in the soil as
microsclerotia
– These can survive
for long periods of
time in the soil
• V. dahliae has a broad
host range
• Strawberry is very
susceptible, 3-12
microsclerotia/g soil
can cause significant
losses.
• Symptom expression
starts in the spring as
the temperatures begin
to warm up
Methyl Bromide Alternatives Research
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Macrophomina (Charcoal Rot)
Macrophomina problems are increasing on fields treated consecutively via drip fumigation (or low application rates). Growers will need to rotate drip applications with broadcast treatments to keep these fields viable for crop production.
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Fusarium (Fusarium wilt)
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Emission Reduction Methods
• Application Methods:
– Deep injection
– Subsurface drip fumigation
– Local area treatment (strip or spot applications)
• Surface Treatment:
– Plastic film (tarp) (impermeable film)
– Irrigation (water treatment/seal)
– Organic amendment (compost, manure, etc.)
– Chemical treatment (e.g., K-thiosulfate)
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Use of “Plastic Mulch” or Tarp for
Soil Fumigation
“Agricultural Film”
• Reduces/delays fumigant volatilization losses
Less emissions rates and smaller buffer
zone
Less total fumigant emissions (total flux)
• Enhances the efficacy of reduced rates by
keeping fumigants in soil for a longer time
• Maintains and possibly enhances yield by
warming/cooling the soil, moisture, etc…
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“Semi-impermeable”
Tri-extruded LDPE
LDPE
LDPE
Polyamide “Virtually impermeable (VIF)”
LDPE + Nylon barrier
LDPE
LDPE
LDPE
LDPE
LDPE
EVOH Admer
Adhesive
“Totally impermeable (TIF)”
5-layer EVOH resin barrier
“Standard” polyethylene
tarp (HDPE or LDPE) LDPE
Agricultural Film Types
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PE/EVOH/PE
5 layer TIF
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Plastic Permeability Measurement Mass Transfer Coefficient
Plastic film is mounted between two chambers
Fumigant is applied to the lower chamber
The cells are kept at a known temperature
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Diffusion of MB through standard LDPE
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lati
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S-Modeled
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R-Measured
Source (lower) chamber
Receiving (top) chamber
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Diffusion of MB through metalized film
Source (lower) chamber
Receiving (top) chamber
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Diffusion of MB through Bromostop VIF
Source (lower) chamber
Receiving (top) chamber
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Mass Transfer Coefficients (cm/h)
(Before and After Tarping)
Film type
Cis 1,3-D Cis 1,3-D Chloropicrin
Before After Before After Before After
Pliant embossed, 1.25 mil 14.61 16.38 17.32 18.22 9.04 9.98
PolyPak Std, 1.5 mil 3.23 3.79 5.15 5.65 1.49 1.70
PolyPak SIF, 2.0 mil 1.42 1.53 1.51 1.71 0.67 1.71
Blockade, 1.25 mil 0.86 0.88 1.65 1.74 0.11 0.17
Bromostop VIF, 1.38 mil 0.07 0.27 0.09 0.42 0.02 0.18
Eval/Mitsui TIF, 1.38 mil 0.00 0.02 0.001 0.07 0.001 0.01
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Various Film Structures
Mono-Layer Blend
LLDPE & MDPE
PE & Tie
PE & Tie
Nylon
Mono-Layer Blend LLDPE,
MDPE, & REPRO
PE
PE
Nylon
TIE
TIE
PE
PE
EVOH
TIE
TIE
PE
PE
EVOH or Nylon
TIE
TIE
PE
PE
STD STD 3-layer
VIF
5-layer
VIF
5-layer
TIF
7-layer
VIF or
TIF
FUMIGANT BARRIER
POOR POOR MEDIUM MED/HIGH MED/HIGH HIGH
PHYSICAL PROPERTIES
GOOD HIGH POOR MEDIUM POOR HIGH
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Approved Tarps for Products Containing Midas
Manufacturer Trade Name Tarp Thickness
(mil)
Cadillac Cadillac VIF 1.25
Filmtech Grozone VIF 1.15
Ginegar Ozgard (black) VIF 1.25
IPG Bromostop VIF 1.30
Klerks Hytibar VIF 1.30
Olefina Guardian VIF 1.20
Pliant Blockade VIF 1.25
Raven VaporSafe TIF 1.00
http://www.cdpr.ca.gov/docs/registration/mei_pdfs/tarp_list_approved.pdf
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Does retentive film (TIF and VIF) reduce
fumigant volatilization losses (flux rate and
total mass loss) from agricultural fields?
Does retentive tarp improve fumigant
distribution (vertical/horizontal) in soil?
Does retentive tarp enhance the efficacy of
lower fumigant application rates?
(concentration x time)
Concerns about using retentive films:
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Wasco, CA. June 2009. Methyl Bromide/Chloropicrin 50:50 with soil moisture at 70% field capacity
Field 5: Deep (18”) broadcast under TIF
Field 4: Deep (18”) strip (50% treated)
under TIF
Field 3: Shallow (12”) broadcast under TIF with
KTS spray
Field 2: Shallow (12”) broadcast under TIF
Field 1: Shallow (12”) broadcast under PE
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1300
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No
rth
-So
uth
Axis
(m
ete
rs)
East-West Axis (meters)
Off-Field Air Quality Monitoring Stations
Meteorological Monitoring Stations
Field layout showing locations of the monitoring stations
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Ch
loro
pic
rin
Flu
x R
ate
(µ
g/m
2/s
ec
)
• Peak for TIF was 51% less than for PE, and occurred during
application (fugitive emissions).
• Post-Application peak on TIF field was 84% reduction from peak
of PE field.
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Chloropicrin Drip Studies Emission reduction with TIF and potassium thiosulfate
Field #
Tarp material
Water seal
Potassium
Thiosulfate
1 Standard LDPE No No
2 TIF (Eval/Mitsui) No No
3 Standard LDPE Yes Yes
4 Standard LDPE Yes No
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Ch
loro
pic
rin
em
issi
on
s R
ate
s (u
g/m
2/s
ec)
Date/Time
Chloropicrin Emission Rates, Salinas, 2007
Standard PE Tarp
TIF (5 layers, Eval/Mitsui)
Standard PE Tarp plus Thiosulfate
Standard PE Tarp plus water treatment
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Waiting period before tarp cutting and removal 1,3-Dichloropropene and Chloropicrin Retention under
Standard Tarp (PE) and Totally Impermeable Film (TIF)
Chloropicrin and 1,3-
Dichloropropene were
shank injected at 12”
under TIF and std PE
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1,3-D Emissions Rates, Ventura, CA 2009
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Em
issi
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Ra
te (
ug
/m^
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ec)
Field 1: standard PE tarp
Field 2: TIF
Tarp cutting
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1,3-D Total Emissions, Ventura, CA 2009
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Date
To
tal
ma
ss l
oss
re
lati
ve
to
am
ou
nt
ap
pli
ed
(%)
Field 1: standard PE tarp
Field 2: TIF
Tarp cutting
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1,3-dichloropropene Emission Rates
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Period
Em
issi
on
Rat
e
(ug/
m2
/sec
)
Field 1 (16 days)
Field 2 (10 days)
Field 3 (5 days)
Lost Hills Flux Study, 2011
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Chloropicrin Emission Rates
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Period
Em
issi
on
Rat
e
(ug/
m2
/sec
)
Field 1 (16 days)
Field 2 (10 days)
Field 3 (5 days)
Lost Hills Flux Study, 2011
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Cumulative Mass loss of 1,3-dichloropropene
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Period
Pe
rcen
t M
ass
Lost
(%
)
Field 1 (16 days)
Field 2 (10 days)
Field 3 (5 days)
Lost Hills Flux Study, 2011
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Cumulative Mass Loss of Chloropicrin
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Period
Pe
rcen
t M
ass
Lost
(%
)
Field 1 (16 days)
Field 2 (10 days)
Field 3 (5 days)
Lost Hills Flux Study, 2011
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Chlo
ropi
crin
Pea
kFl
ux R
ate
(µg/
m2 /
sec)
Pre-GAP Shank Flux Studies
GAP-Compliant Shank Studies
Drip Application Studies
Current Chloropicrin Field Volatility Dataset: 36 flux studies Good Agricultural Practices (GAPs)
All 26 GAP-compliant shank studies had peak flux rates lower than tarped drip, regardless of tarp/non-tarp, deep/shallow, broadcast/bed.
Only one study had a higher peak than Tarped Drip:
Non-Tarped Buried Drip
Since GAPs are now mandatory on labels, USEPA no longer has “pre-GAP” buffer zones on labels.
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USEPA Buffers distances are subjectively large; want users to utilize emissions
reduction strategies. Developed Buffer Zone Reduction Credits.
% Reduction in Chloropicrin Buffer Zone
Condition Chloropicrin
Use of specific high
barrier tarp
20% (metalized films), 40% (nylon VIFs),
or 60% (high-end VIFs and all TIFs)
Organic matter content 10% (OM ≥ 1% - 2%), 20% (OM >2 – 3%), 30%
(OM > 3%)
Clay content > 27% 10%
Soil temp ≤ 50oF (shank) 10%
Potassium thiosulfate 15%
Water seal 15%
Max reduction 80%
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Summary
Low permeability tarps (TIF and VIF) can
significantly reduce emissions as well as
improve efficacy because it can retain
high fumigant concentration under that
tarp.
Delayed tarp cutting will reduce peak flux
and total emissions:
~10 days chloropicrin
~15 days 1,3-D (Telone)
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• California Strawberry Commission
• Cal-EPA (DPR)
• USEPA
• USDA-ARS, Area Wide Project
• Almond Board of California
• TriCal, Inc.
Acknowledgement
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Thank you very much
Husein Ajwa
1636 East Alisal Street, Salinas, CA 93905
Phone (831) 755-2823
FAX (831) 755-2844