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Resource Guide for Organic Insect and Disease ... - Cornell University

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164 <strong>Organic</strong> <strong>Resource</strong> <strong>Guide</strong><br />

accurately measure the required amount of Entrust SC, a graduated cylinder is required, allowing<br />

measurements of volumes to the nearest one-tenth of a milliliter. Alternatively, a scale can<br />

be used to measure weights to the nearest one-tenth of a gram. Mixing only as much spray as<br />

needed <strong>for</strong> a single treatment is recommended. Do not use more than 3 gallons of spray per<br />

1000 sq ft of area. Follow all other label instructions <strong>for</strong> mixing <strong>and</strong> application.<br />

milliliters (mL) or grams (g)<br />

Entrust SC, per gallon per 3 gallons of per 5 gallons<br />

fl oz/acre of spray spray or 1000 sq ft of spray<br />

2 0.5 1.4 2.3<br />

3 0.7 2.0 3.4<br />

4 0.9 2.7 4.5<br />

5 1.1 3.4 5.7<br />

6 1.4 4.1 6.8<br />

7 1.6 4.8 7.9<br />

8 1.8 5.4 9.1<br />

9 2.0 6.1 10.2<br />

10 2.3 6.8 11.3<br />

According to the manufacturer, the rate of 7 fluid ounces per acre is equivalent to 1 teaspoon<br />

per 1,000 square feet. Dow. (2012)<br />

Studies have shown that some populations of the diamondback moth have developed resistance<br />

when Entrust is used intensively (Zhao et al. 2002), so resistance management should<br />

be practiced. Avoid applications of Entrust on consecutive pest generations. Alternate sprays<br />

with other effective products, <strong>and</strong> implement cultural controls. The Entrust label has detailed<br />

instructions <strong>for</strong> resistance management.<br />

Many crops have maximum yearly application restrictions. See the label <strong>for</strong> specific in<strong>for</strong>mation.<br />

REENTRY INTERVAL (REI): 4 hours.<br />

EFFECTS ON THE ENVIRONMENT<br />

Leaf persistence: Spinosad is partly taken up by leaf tissue, which enhances its effectiveness<br />

over time. Dry surface residues do little harm to non-plant feeding insects. Spinosad residues<br />

on the leaf surface are broken down by sunlight. Half-lives <strong>for</strong> spinosyn A are 1.6 to 16 days,<br />

depending on the amount of sunlight received (Saunders & Brett 1997).<br />

Fate in water: When spinosad is mixed with water, very little breakdown (hydrolysis) occurs;<br />

however, in water exposed to sunlight, photodegradation occurs rapidly (Saunders & Brett<br />

1997). In the absence of sunlight, the half lives of spinosyn A <strong>and</strong> D are at least 200 days.<br />

Soil Persistence: Soil microbes degrade spinosad into other spinosyns that can persist in the<br />

soil <strong>for</strong> several months <strong>and</strong> remain biologically active. Repeated applications could lead to<br />

some build-up of spinosyns in soil. A 10-month field study in Cali<strong>for</strong>nia <strong>and</strong> Mississippi showed<br />

that no degradation products were found in soil below 24 inches (Saunders & Brett 1997).<br />

Leaching: Spinosyn A is more water-soluble than spinosyn D; there<strong>for</strong>e, it was the subject of<br />

soil mobility studies. Research showed that spinosyn A <strong>and</strong> its soil metabolites bind to soil <strong>and</strong><br />

have low soil mobility.<br />

Wildlife: Spinosad shows slight toxicity to birds, moderate toxicity to fish, <strong>and</strong> slight to moderate<br />

toxicity to aquatic invertebrates. In laboratory tests, it was highly toxic to bees, oysters (US<br />

EPA 1997 a,b), <strong>and</strong> other marine mollusks (Dow 2001).

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