Reducing Fumigant Application Rates and Soil Emissions with Plastic Mulch Technology 1

Similar documents
Chapter 6. Alternatives to Methyl Bromide Soil Fumigation for Florida Vegetable Production

Water and Nitrogen BMPs for Tomato and Watermelon: Water Quality and Economics 1

Nematode Management in Sweet Corn 1

Paladin, Pic-Clor 60, and Pic-Clor 80 (Chloropicrin): Drip- and Shank-applied under Retentive Film for Strawberry Production in California

2. J. W. Noling, professor, Department of Entomology and Nematology; UF/IFAS Citrus Research and Education Center, Lake Alfred, FL

Nematode Management in Onions 1

Nematode Management in Sweet-Corn 1

Maryland May 21, 2009 R. David Myers

Production Budget for Tomatoes in Southwest Florida 1

Production Budget for Tomatoes in the Manatee-Ruskin Area of Florida 1

New Masterbatch for Barrier Films

Nematode Management in Carrots 1

Cotton Cultural Practices and Fertility Management 1

Status of Soil Fumigants

R. Allen Straw, SW VA AREC, VPI Farm Rd., Glade Spring, VA 24340,

The 1/128th of an Acre Sprayer Calibration Method 1

Blossom-End Rot in Bell Pepper: Causes and Prevention 1

California Strawberry Commission Research Program. California Strawberry Commission

02.1 Soil preparation Solarization Sterilization 7

Review of Current Sugarcane Fertilizer Recommendations: A Report from the UF/IFAS Sugarcane Fertilizer Standards Task Force 1

Field Soil Fumigation Issues. Monterey County

Reducing Near-field Agricultural Fumigant Emissions Through Efficacious Changes in Regional Application Practices

Irrigated Acreage in Florida: A Summary through

Relationship of Cow Size to Nutrient Requirements and Production Management Issues 1

Smart Vapor Retarders

A Guide to Collecting Soil Samples for Farms and Gardens

PEACE OF MIND PLASTICULTURE. RELIABILITYStrength PLASTICULTURE

Comparative Costs of Growing Citrus in Florida and Sao Paulo (Brazil) for the Season 1

Screen Filters in Trickle Irrigation Systems 1

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY WASHINGTON D.C., 20460

SOIL FUMIGANTS FOR CONTROL OF PHYTOPHTHORA ROOT ROT

Fumigation Operations

Chapter 4. Nematodes and Their Management

Economic Impacts of Drought on the Florida Environmental Horticulture Industry 1

Cogongrass (Imperata cylindrica) Biology, Ecology, and Management in Florida Grazing Lands 1

Flexible Vapor Control Solves Moisture Problems of Building Assemblies - Smart Retarder to Replace the Conventional PE-Film

Use of Amphibians as Indicators of Ecosystem Restoration Success 1

Floridian Consumer Perceptions of Local Versus Organic Ornamental Plants 1

Technical Bulletin No. 110 GAS BARRIER PROPERTIES OF RESINS

August 14, Brian Leahy Director California Department of Pesticide Regulation 1001 I Street Sacramento, CA

Polymer Composite Gasoline Tanks

MASTERBATCHES. Masterbatch Application and Selection Guide for Irrigation Pipes

Weed Management in Pear 1

Manure is recognized: Solarization and use of compost in vegetable crops. Manure production. Why manure is a problem today but was not 50 years ago

Stormwater as an Alternative Source of Water Supply: Feasibility and Implications for Watershed Management 1

World, U.S. and Florida Avocado Situation and Outlook 1

THE INTRODUCTION THE GREENHOUSE EFFECT

Estimating Volatile Organic Compound Emissions from Pesticides using PUR data. March 2006 Frank Spurlock

2015 COST ESTIMATES OF ESTABLISHING AND PRODUCING RED RASPBERRIES IN WASHINGTON STATE

Crop Protection Research Institute

A top issue: Quality. Manual of Tomato and Eggplant Field Production

Natural Resources Conservation Service

Barrier Coating Options. English

Herbicide Physiology: Why do I see what I see?

Green Manure Cover Crops Between Rows of Widely Spaced Vegetable Crops

High tunnels, also referred to as hoop houses,

Weed control reality. Landscape weed control James Altland Oregon State University. Redroot pigweed. Weeds. Landscape weed control

Nitrogen Transformation Inhibitors and Controlled Release Urea

Validation of an Area-Wide Extension Program to Estimate the Seasonal Abundance of Adult Citrus Root Weevils with Unbaited Pyramidal Traps 1

Conservation Practices. Conservation Choices. These five icons will show the benefits each practice offers... 6/4/2014

Herbicidal weed control

Guidelines for Purchase and Application of Poultry Manure for Organic Crop Production 1

Development and Optimization of the Steam Auger for Management of Almond Replant Disease in the Absence of Soil Fumigation

RETROFIT INSULATION in WOOD ROOFS

ECONOMIC ANALYSIS OF TEMIK ON CITRUS IN THE INDIAN RIVER AREA IN SOUTHEASTERN FLORIDA. Lindsey Blakeley, Richard Weldon, and Gary Fairchild

IR-4 MINOR USE PERFORMANCE FORM PR NO. Date of Report Field I.D. No. Page 1

Of vital importance..

Assessment of blackcurrant bush size and wood quality to aid with N recommendations

Rice-rice-potato rotation system

Principle Investigators:

Introduction... 2 Asparagus... 4 Basil... 5 Beans, Speciality Green... 6 Carrots... 7 Eggplant... 8 Garlic... 9 Greens, Salad Peas, Snow...

4-H SWINE RECORD BOOK 2

ECONOMIC ANALYSIS OF ALDICARB ON CITRUS IN THE INDIAN RIVER AREA IN SOUTHEASTERN FLORIDA. Lindsey Blakeley, Richard Weldon, and Gary Fairchild

Field Fumigation Update

Resources Conservation Practices Tillage, Manure Management and Water Quality

Overview of Florida s s Commercial Blueberry Industry. Jeff Williamson Horticultural Sciences Department IFAS, University of Florida

EXPERIMENTAL SITE AND METHODS

CORN BEST MANAGEMENT PRACTICES APPENDIX A. Corn Planting Guide

Crossbreeding Systems in Beef Cattle 1

Introduction of EVAL EVOH for Geosynthetics 2011

Transportation Management

Glyphosate. on Potatoes. Effect of A1642

33. Fate of pesticides in soil and plant.

Landscape Weed Management Goals

Management of Soil and Water for Vegetable Production in Southwest Florida 1

Interpreting Nitrate Concentration in Tile Drainage Water

Calcium Carbonate in Blown HDPE Film

Manure Spreader Calibration

WE OFFER: UV stabilizers Clarifiers or nucleating Odour absorbers Antistatics Flame retardants Antiblocks Foaming agents Dessicant MFI modifiers

NRCS Conservation Programs Update

DEMONSTRATION STAGE ON MB ALTERNATIVES FOR STRAWBERRY PRODUCTION IN HUELVA (SPAIN). J.M. López-Aranda (1)*, J.J. Medina (2) and L.

NOMEX TYPE 410 TECHNICAL DATA SHEET. Electrical properties. Please note: PERFORM WHEN THE HEAT S ON TYPICAL ELECTRICAL PROPERTIES

Chemical Name: Manufacturer: Container size: Location: Disposal:

Sunflower Seeding Rate x Nitrogen Rate Trial Report

Tex-121-E, Soil-Lime Testing

Progress Report (task 3) Project Title: BMPs for Florida blueberries. Contract # : Dorota Z. Haman Agricultural and Biological Engineering

EVALUATING WATER REQUIREMENTS OF DEVELOPING WALNUT ORCHARDS IN THE SACRAMENTO VALLEY

Comparison of Atmospheric Plasma and Corona Treatments in Promoting Seal Strength

COGENERATION PLANT FAQ. What is biomass cogeneration? Cogeneration is the simultaneous production of electricity and heat using a single primary fuel.

HIGH PERFORMANCE LINING FOR BULK MATERIAL HOPPER

Transcription:

ENY046 Reducing Fumigant Application Rates and Soil Emissions with Plastic Mulch Technology 1 J. W. Noling 2 Fumigants such as methyl bromide, chloropicrin, metam, and 1,3-Dichloropropene have been used in combination with plastic mulch row covers since the early 1960s for broad spectrum, soilborne pest and disease control. Federal label restrictions for use of methyl bromide and other fumigants now require the installation of plastic mulch covering immediately following application. Use of agricultural plastic films (tarps) to cover the treated field after fumigation has been a common practice to reduce the fumigant emission and to minimize worker exposure to the fumigants. During the recent federal re-registration of soil fumigants, the United States Environmental Protection Agency (EPA) established a new set of regulations requiring a suite of complementary mitigation measures to protect handlers, re-entry workers, and bystanders from risks resulting from exposure to the soil fumigants. Among the new requirements is the need for a buffer zone between treated and untreated sites to allow airborne fumigant residues to disperse before they reach bystanders. EPA is also granting buffer zone credits, which reduce buffer distances, to encourage fumigant users to employ practices that reduce emissions, such as with the use of high-barrier tarps. EPA, however, will only recognize use of specific high-barrier metalized, virtually impermeable (VIF), or totally impermeable (TIF) mulch films that meet EPA-approved emission reductions to qualify for these buffer-zone-reducing credits. With the new fumigant regulations and rising cost of crop production, including fumigants, it would be desirable to reduce the standard use rate of soil fumigants, particularly where the new fumigant labels impose more stringent buffer zone restrictions (near schools, clinics, prisons) and where fumigant shortage or use caps further restrict possible allocation and use. Plastic Mulch Bed Covers The most commonly used plastic mulches in Florida are black and white polyethylene (PE) mulches typically in the range of 0.6 to1.4 mil thick. Many different colors, thicknesses, and widths of these embossed PE plastic mulches are available for agricultural use. In general, the advantages of plastic mulch include: 1) thermal regulation of soil temperature; 2) weed suppression; 3) increasing the effectiveness of soil-applied pesticides; 4) maintenance of bed shape and architecture and provision of drainage; 5) barrier protection of fruit from soil pathogens; 6) minimization of root pruning from tillage operations for weed control; 7) minimization of the evaporative loss of water from soil; and 8) reduction of leaching of fertilizers from the root zone of plants. In general, the plastic mulch layer protects crops from environmental extremes and impact and serves to accelerate plant growth and increase crop yields. In addition to the horticultural advantages, plastic mulches also serve to delay the volatilization of fumigant gases from soil and reduce emissions into the atmosphere. In practical 1. This document is ENY046, one of a series of the Department of Entomology and Nematology, UF/IFAS Extension. Original publication date October 2001. Revised March 2013. Reviewed December 2012 and December 2016. Visit the EDIS website at http://edis.ifas.ufl.edu. 2. J. W. Noling, professor, Entomology and Nematology Department, UF/IFAS Citrus Research and Education Center, Lake Alfred, FL 33850. The Institute of Food and Agricultural Sciences (IFAS) is an Equal Opportunity Institution authorized to provide research, educational information and other services only to individuals and institutions that function with non-discrimination with respect to race, creed, color, religion, age, disability, sex, sexual orientation, marital status, national origin, political opinions or affiliations. For more information on obtaining other UF/IFAS Extension publications, contact your county s UF/IFAS Extension office. U.S. Department of Agriculture, UF/IFAS Extension Service, University of Florida, IFAS, Florida A & M University Cooperative Extension Program, and Boards of County Commissioners Cooperating. Nick T. Place, dean for UF/IFAS Extension.

reality, however, the PE mulches in common use today in Florida actually provide little direct physical barrier to the diffusion of most fumigants through the mulch. The condensation of water on the under surface of the film and the resultant increased moisture content within surface soil appears to be actually more important for slowing the volatilization of these fumigants from soil than the mulch itself. The water seal that forms on the soil surface acts as a diffusion barrier because diffusion of a gas through water is much less and slower than diffusion through open soil pores. Similarly, beds that are moist and tightly compressed are much more resistant to fumigant diffusion than beds that are dry and only loosely compacted or pressed. Emissions of Soil Fumigants from Agricultural Fields In recent years, many different field studies have been conducted to obtain information on soil fumigant emissions from bare and mulch-covered soil following field application. Much of this research appears to show that as much as 20 to 90% of a fumigant like methyl bromide applied to a given field can ultimately out-gas through the PE plastic mulch cover and into the air after soil fumigation. Many different chemical, soil, and environmental factors interact to cause the wide variation of reported emission losses from soil with any of the currently used fumigant compounds. In general, the rate at which a specific fumigant volatilizes from soil under typical conditions is initially high following application and then decreases with time, such that after 7 to 14 days post application, little remains in soil (Figure1). After application, volatilization continues as long as the fumigant remains in the soil and a concentration-difference exists under the plastic and the lower air of the field. With methyl bromide, a large proportion of the methyl bromide applied volatilizes from soil within the first 24 to 48 hours following application. Most other fumigants with lower vapor pressure require considerably longer to diffuse and completely dissipate from soil. Since temperature has such a direct effect, the highest levels of fumigant outgassing typically occur during the middle of the day, when air temperatures are highest. Outgassing levels are lowest at night, when air temperatures are coolest. The use of higherbarrier, gas-impermeable mulches may make it possible to reduce fumigant application rates by helping to contain the fumigant longer within the soil and reduce overall emissions into the atmosphere. Figure 1. Generalized representation of the relative emissions of a soilapplied fumigant volatilizing through a plastic-polyethylene mulch cover with time after initial soil fumigation. Data is plotted only to show general decline in emissions with time, and highest daily rates of emission occurring midday and lowest emissions at night. Besides temperature, other soil and environmental conditions can greatly modify fumigant emissions from soil. Mulch Permeability The permeability (the ability to pass through) of a plastic mulch to any soil fumigant is technically and quantitatively expressed as a mass transfer coefficient (MTC), which is dependent only upon the properties of the film (thickness, density, chemical composition), the properties of the fumigant, and physical conditions of the environment (such as temperature and humidity). Regardless of composition, thicker mulches are generally less permeable to a soil fumigant than are thin mulches (Figure 2). In most cases, practical and cost-efficiency considerations prevent the use of thicker PE mulches for enhanced containment of a fumigant in soil. Figure 2. Permeability of methyl bromide (Mebr), Chloropicrin (Plc), and two isomers of 1,3-Dichloropropene (Telone ) through highdensity polyethylene (HDPE) plastic mulch of two thicknesses. Taller bars indicate higher permeability. Among the different commercially available plastic mulch films (Table 1), some films provide a better diffusion barrier to certain fumigants than others (Figures 2 and 4). PE films 2

are the group with the highest permeability. Even within the PE group, the high-density polyethylene (HDPE) films can be differentially (more or less) permeable to a variety of different fumigants (Figure 2). Metalized films follow as a group with barrier properties characterized as only moderately permeable. The VIF films are considered in a group with very low permeability, allowing very little of a fumigant gas to pass through it, and, as the name implies, are virtually impermeable. TIF films belong to a group where measured permeability is typically defined as being negligible (Figure 3). Figure 3. Relative permeability of fumigant gases through polyethylene (PE), metalize, virtually impermeable (VIF) and totally impermeable (TIF) plastic mulch films. Taller bars indicate higher permeability. Figure 4. Permeability of methyl bromide (Mebr), iodomethane (IOD), two isomers of 1,3-Dichloropropene (Telone ), dimethyl disulfide (DMDS) (Paladin ), methyl isothiocyanate (MITC)( Vapam, KPam ), and Chloropicrin (PlC), through polyethylene (PE), metalized, virtually impermeable (VIF) and totally impermeable (TIF) plastic mulch films. Higher values indicate higher permeability. Note differences in Y-axis scales between panels and mulch film types representing very significant orders of magnitude differences in permeability. These VIF and TIF mulches are typically multi-layer films composed of barrier polymers such as ethylene vinyl alcohol (EVOH) or polyamide (nylon) sandwiched between other polymer layers (typically PE) that keep the barrier polymers from swelling. Compared to PE mulch films, VIF and TIF films are oftentimes over 20,000 times less permeable to a variety of fumigant compounds (Figure 4). The permeability of the different mulch films (Table 1) to different fumigants can vary considerably, providing a reasonable barrier for one fumigant but not another (Figure 4). For example, some of the high-barrier, high-density polyethylene mulches provide some resistance to methyl bromide and chloropicrin but were shown to offer less resistance to 1,3-D (Telone ) diffusion (Figure 2). MITC, the active ingredient of metam sodium (Vapam ) and metam potassium (KPam ), is even more diffusive than Telone through a variety of different mulch film types compared to methyl bromide, methyl iodide (IOM), or chloropicrin (Figure 4). In Florida mulch trials, monitoring of soil gas concentration and persistence was able to differentiate, relative to low Figure 5. Soil air concentrations of iodomethane (methyl iodide) under different low-density polyethylene (LDPE), metalized, and virtually impermeable (VIF) plastic mulch films monitored over a seven-day period. Note higher soil air concentration over time within response curves for the VIF and metalized mulch films compared to LDPE. density PE, the general retentiveness of 12 different gasimpermeable plastic mulches to the soil fumigant methyl iodide (iodomethane) (Figure 5). With this fumigant and others that were tested, the low-density PE mulch film was characterized as the least retentive of the mulches evaluated, 3

with the fumigant generally dissipating completely from soil within 3 to 4 days. All of the different metalized and VIF mulch films produced higher soil air concentrations (ppm) over a longer period of time (>7 days) than soil air concentrations produced under low-density PE. The benefits of using the high-barrier metalized and VIF films during fumigation has been documented in this as in many other studies to enhance fumigant efficacy by retaining fumigants in the soil for longer periods of time. Research on the use of various types of high-barrier mulches to reduce soil application rates and emissions of methyl bromide has also been conducted in many different locations nationally and around the world. For example, use of virtually impermeable plastic mulches (VIF) has proved to be a simple and effective strategy to reduce soil emissions of not only methyl bromide but of other fumigant gases as well. It is clear from the research that has been conducted with VIF and TIF that fumigant use rates can be substantially reduced without serious consequence to pest control efficacy or crop yield response. The results of most of these field studies show that fumigant application rates can be reduced by 20 to as much as 40% through the use of virtually impermeable or the more gas-tight TIF mulch films at the time of application. These high-barrier mulches cannot always be used without problems, however. detection of any fumigant in soil air suggests a potentially serious problem with an appropriate delay in planting to avoid issues of plant damage and mortality. The specific high-barrier mulch film products and names of the principal manufacturers or their US distributors are listed in Table 1. Additional updated information regarding EPA-approved plastic mulch films or tarps for soil fumigant uses can be found at: http://www.epa.gov/pesticides/ reregistration/soil_fumigants/ Potential Problems with High- Barrier Mulches Historically, VIF and TIF mulches have suffered from high cost and from other problems involving tensile strength. They were often slow to properly install and were subject to tearing (zippering) during machine application in the field. Most of these problems have been resolved. However, other problems that can and do frequently occur involve delays in fumigant dissipation from soil and a phytotoxic response to young seedlings and transplants transferred to soils containing phytotoxic soil residues of the fumigant. For example, fumigants containing 1,3-dicloropropene (an active ingredient in several fumigant products, including Telone II, Telone C-35, and PicClor 60 ) can have a long plant-back interval if a high-barrier VIF or TIF mulch film is used, particularly if the soil remains wet or cool after application. In this scenario, the fumigant is trapped under an impermeable barrier, preventing its volatilization and escape from the soil. The more efficient containment of gases below the mulch suggests that soil air concentrations of the fumigants should be monitored and that plantings may have to be delayed to ensure that soil residues have dissipated and plant injury will not occur. At present the 4

Table 1. Selected manufacturers or vendors of a variety of polyethylene mulch films (PE), metalized films, virtually impermeable films (VIF), and totally impermeable plastic mulch films. Films represent different thicknesses (mil), colors, embossing, and barrier layers. Polyethylene Films (PE): AEP Sun Film High Barrier 1.0 mil, clear polyethylene AEP Inc. Cadillac HDPE 1.25 mil, clear Cadillac Products Packaging Co. Canslit Embossed HDPE 0.6 mil, black Canslit Inc./Imaflex Inc. Canslit Embossed LDPE 1.25 mil, black Canslit Inc./Imaflex Inc. Pliant Embossed LDPE 1.25 mil, embossed LDPE Pliant Corp Metalized Films: Canslit Metalized 1.25 mil, black/silver Canslit Inc./Imaflex Inc. Canslit Metalized 1.25 mil, white/silver Canslit Inc./Imaflex Inc. Pliant Metalized 1.25 mil, black/silver Pliant Corp Virtually Impermeable Films (VIF): Cadillac VIF 1.25 mil, black Cadillac Products Packaging Co. Can-Block VIF 0.8 mil, black Canslit Inc./Imaflex Inc. FilmTech VIF 1.25 mil, black FilmTech Corp. Ginegar Ozgard 1.25 mil, black Ginegar Plastic Products, Ltd. Ginegar VIF 1.25 mil, embossed black Ginegar Plastic Products, Ltd. Guardian Olefinas VIF 1.2 mil, embossed black Guardian Agroplastics Olefinas USA MidSouth VIF 1.25 mil, embossed black Mid South Extrusion Pliant Blockade Black 1.25 mil, black Pliant Corp Pliant Blockade White 1.25 mil, white/black Pliant Corp Totally Impermeable Films (TIF): AEP-One EVOH barrier, 1.0 mil, clear AEP Inc. Berry EVOH-High Barrier EVOH barrier, black Berry Plastics Berry High Barrier w/improved toughness EVOH barrier, black Berry Plastics Berry EVOH-Supreme Barrier EVOH barrier, black Berry Plastics Dow SARANEX A black Dow Chemical Co. Dow SARANEX B black Dow Chemical Co. Klerks/HyPlast TIF clear Klerk s Plastic/HyPlast Raven TIF VaporSafe 1.0 mil, EVOH barrier, clear Raven Industries Inc. Raven TIF VaporSafe 1.4 mil, EVOH barrier, black Raven Industries Inc. Additional information regarding EPA-approved plastic mulch films or tarps for soil fumigant uses can be found at: http://www.epa.gov/ pesticides/reregistration/soil_fumigants/ 5