Carbaryl, Carbofuran, and Methomyl - National Marine Fisheries ...

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use on fruits, and vegetables). Additionally, some uses do not specify the maximum number of applications (e.g., prickly pear, ticks, and grasshoppers). Table 1. Registered uses and application rates for carbaryl in California, Idaho, Oregon, and Washington (EPA 2007) Application Use Site Maximum Single Application Rate (lb a.i./acre) 26 Maximum Number of Applications Minimum Application Interval (days) Maximum per year (lb a.i./acre) Home Lawn 9.1 2 7 Not specified Fire ants 7.4 2 7 Not specified Flower beds around buildings Lawns, recreation areas, golf 8 4 None 6 courses, sod farms, commercial lawns 8 2 7 8 Parks 8 1 - 8 Citrus 12 1 - 12 Citrus 7.5 8 14 20 Olives 7.5 2 14 Not specified Almonds, chestnuts, pecans, filberts, walnuts, pistachio 5 4 7 15 Flowers, shrubs 4.3 3 7 Not specified Apricot, cherries, nectarines, peaches, plums, prunes 4 (5 dormant) 3 + 1 dormant 15 9 + 5 dormant spray Apple, pear, crabapple, oriental pear, loquat 3 8 14 Not specified Sweet corn 2 8 3 Not specified Caneberries, blueberries, grapes, strawberries 2 5 7 Not specified Tomatoes, peppers, eggplant 2 7 7 8 Peanuts Broccoli, cauliflower, cabbage, 2 5 7 8 kohlrabi, Chinese cabbage, collards, kale, mustard greens, brussel sprouts, hanover salad 2 4 6 7 Sweet potato 2 8 7 8 Field corn, pop corn Leaf lettuce, head lettuce, 2 4 14 8 dandelion, endive, parsley, spinach, swiss chard Celery, garden beets, carrots, 2 5 7 6 horseradish, parsnip, rutabaga, potato, salsify, root turnip, radish 2 6 7 Not specified Prickly pear 2 As needed 7 6 Rice Fresh beans, dry beans, fresh 1.5 2 7 4 peas, dry peas, cowpeas, fresh southern peas, soybeans 1.5 4 7 6 Sugar beets, pasture, grass for seed 1.5 2 14 3 Alfalfa, birdsfoot trefoil, clover 1.5 1/cutting None Not specified Rangeland 1 1 - 1 Cucumber, melon, pumpkin, squash, roses, other herbaceous 1 6 7 Not specified
Use Site plants, woody plants CRP acreage, set-aside acreage, rights-of-way, hedgerows, ditch banks, roadsides, wasteland Non-urban forests, tree plantations, Christmas trees, parks, rangeland trees, rural shelter belts Maximum Single Application Rate (lb a.i./acre) 27 Maximum Number of Applications Application Minimum Application Interval (days) Maximum per year (lb a.i./acre) 1 2 14 3 1 2 7 Not specified adult mosquitoes 10 1 * * Not specified Ticks 2 As needed None Not specified Grasshoppers 1.5 As needed None Not specified flax 1.5 2 14 Not specified Home fruits and vegetables 1.95 6 None 12.1 Proso millet, wheat 1.5 2 14 Not specified lentils 1.5 4 7 Not specified Oyster beds 8 Not specified None Not specified Sunflower 1.5 2 7 Not specified Tobacco 2 4 7 Not specified * Number of applications and interval as specified for use site (pastures, rangeland, forests and wastelands, etc.). Metabolites and Degradates. The major metabolite of carbaryl degradation by both abiotic and microbially mediated processes is 1-naphthol. This degradate represented up to 67% of the applied carbaryl in degradation studies. It is also formed in the environment by degradation of naphthalene and other polyaromatic hydrocarbon compounds. EPA reports that only limited information on the environmental transport and fate of 1-naphthol is available and indicates this compound is less persistent and less mobile than the parent carbaryl (EPA 2003). Carbofuran Carbofuran is a NMC systemic pesticide first registered in the U.S. in 1969. The BE for carbofuran indicates it is registered as a restricted use broad spectrum insecticide, nematicide, and miticide for use on a wide variety of agricultural and non-agricultural crops (EPA 2004). Carbofuran is classified as a restricted use pesticide and is formulated into flowable, wettable powder, and granular forms. Through an agreement between EPA and the technical registrant in 1991, granular carbofuran has been limited to the sale
Page 1 and 2: Ms. Debbie Edwards Director, Office
Page 3 and 4: National Marine Fisheries Service E
Page 5 and 6: Snake River Spring/Summer-Run Chino
Page 7 and 8: Commercial, Recreational, and Subsi
Page 9 and 10: Critical Habitat Risk Hypotheses ba
Page 11 and 12: Table of Figures Figure 1. Stressor
Page 13 and 14: Table of Tables Table 1. Registered
Page 15 and 16: Table 31. Area of Land Use Categori
Page 17 and 18: Table 67. . Examples of published f
Page 19 and 20: Agency: Activities Considered: Nati
Page 21 and 22: This Opinion is based on NMFS’ re
Page 23 and 24: activities that may improve EPA’s
Page 25 and 26: affect but is not likely to adverse
Page 27 and 28: On November 13, 2008, EPA provided
Page 29 and 30: On January 21, 2009, the agencies a
Page 31 and 32: in California, Idaho, Oregon, and W
Page 33 and 34: On that same date, EPA e-mailed NMF
Page 35 and 36: After registering a pesticide, EPA
Page 37 and 38: isk assessment. With these and othe
Page 39 and 40: Typically, formulations are combine
Page 41 and 42: EPA also issued generic and product
Page 43: pecans, peppers, pistachios, plums,
Page 47 and 48: are subject to a four year phase-ou
Page 49 and 50: Table 2. Registered uses and applic
Page 51 and 52: mildews and other fungal diseases.
Page 53 and 54: methomyl are 32.4 lb a.i./acre/year
Page 55 and 56: would not likely adversely affect C
Page 57 and 58: In the final steps of our analyses,
Page 59 and 60: Evidence Available for the Consulta
Page 61 and 62: sustaining in the natural environme
Page 63 and 64: Stressors of the Action (see Figure
Page 65 and 66: Species Risk Hypotheses We construc
Page 67 and 68: habitats is then assessed. This por
Page 69 and 70: The problem formulation phase as ar
Page 71 and 72: Risk Characterization We follow the
Page 73 and 74: the probability of risk. In the Ris
Page 75 and 76: Figure 5. Map showing extent of inl
Page 77 and 78: Opinion. Summaries of the status an
Page 79 and 80: Chinook salmon are dependent on the
Page 81 and 82: Eureka Figure 6. CC Chinook salmon
Page 83 and 84: Table 6. CC Chinook salmon--prelimi
Page 85 and 86: Table 7 identifies populations with
Page 87 and 88: The CV drainage as a whole is estim
Page 89 and 90: have greatly reduced or eliminated
Page 91 and 92: Portland Salem Figure 9. LCR Chinoo
Page 93 and 94: important life history type remains
Page 95 and 96:
Table 9. UCR Chinook salmon - preli
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In the most recent five-year geomet
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Figure 11. Puget Sound Chinook dist
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Status and Trends Puget Sound Chino
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flow, temperature, sediment load, w
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San Francisco Figure 12. Sacramento
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of historic spawning areas. Additio
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Status and Trends SR fall-run Chino
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Critical Habitat Critical habitat f
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Portland Seattle Spokane Figure 14.
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and five-year old fish, after two t
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surface and ground water and degrad
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Life History UWR Chinook salmon exh
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Bay, California. Historically, chum
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quality in the freshwater, estuarin
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Life History Chum salmon return to
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catastrophic events. Overall, the p
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Figure 17. Hood Canal Summer-run Ch
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improvements in 2000, with upward t
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ground water and degrade water qual
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San Francisco Figure 18. CCC Coho s
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Information on the abundance and pr
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Table 16 identifies populations wit
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Life History Although run time vari
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programs. The three major river sys
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Data on population abundance and tr
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Figure 21. Oregon Coast Coho salmon
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Preliminary spawner survey data for
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channels, backwaters, terrace tribu
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Figure 22. Ozette Lake Sockeye salm
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the 1997 status review due to resam
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Seattle Portland Figure 23. SR Sock
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Adult returns to Redfish Lake durin
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esume migration in early spring to
Page 163 and 164:
Central California Coast Steelhead
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Status and Trends The CCC steelhead
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San Francisco Figure 25. California
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and Jackson 1996; McEwan 2001). Ste
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Olympia Portland Salem Figure 26. L
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hatchery fish in naturally-spawning
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species includes the only populatio
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Life History Most MCR steelhead smo
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Critical Habitat Critical habitat w
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Eureka Figure 28. Northern Californ
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may affect steelhead migration patt
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Of the 21 populations in the Puget
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Seattle Spokane Figure 30. SR Basin
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and spawner estimates for the Tucan
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San Jose Figure 31. S-CCC steelhead
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Figure 32. Southern California stee
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extinction,” with the remaining 1
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Portland Figure 33. UCR Steelhead d
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“low” for the Wenatchee and Met
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Figure 34. UWR Steelhead distributi
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Molalla/Pudding, Yamhill, Tualatin,
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Natural Mortality Factors Available
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Marine Mammal Predation Marine mamm
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downstream of Bonneville Dam. Socke
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Oceanographic Features and Climatic
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coincides with relatively poor ocea
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from streams in watersheds with agr
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chemicals used has decreased (Table
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California, Idaho, Oregon, and Wash
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to disease, decrease the ability of
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characterized by emergent aquatic p
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subregions and accounting units for
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Region USGS Subregion Central Calif
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Table 31. Area of Land Use Categori
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Table 33. Land uses and population
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(Table 34). See species ESU/DPS map
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undeveloped sites in the Santa Ana
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and grazing. Dams and water diversi
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Artificial Propagation Anadromous f
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water resources is handled by Calif
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containers at time of use. • Cond
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Table 36. Area of land use categori
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Columbia River Basin The most notab
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Ranching practices have led to incr
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17% of mainstem Yakima River sample
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detected in samples from all sites,
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Whitney 1979). Similarly, over one
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nation’s silver output has come f
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(USBR 1998 in (FCRPS 2008); providi
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The States of Oregon and Wasington
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Columbia River chum salmon are not
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including brown and brook trout, At
Page 267 and 268:
density residential with some agric
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Although urban areas occupy only 2%
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Habitat Modification Much of the re
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Table 42. Pollutants of Concern in
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the 1950s. The vast majority of the
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pugettensis). An NPDES permit is re
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Habitat loss through wetland fills
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afted and moved to market or downst
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Oregon is in the process of develop
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Effects of the Proposed Action The
Page 287 and 288:
Carbaryl dissipates in the environm
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high water solubility, low Kow, and
Page 291 and 292:
Table 46. Environmental fate charac
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Species General Life History Descri
Page 295 and 296:
Table 48. Examples of registered us
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Table 49. PRZM-EXAMS exposure estim
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estimate do not represent the highe
Page 301 and 302:
BE provides a peak EEC of 5.5 μg/L
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alcoves, channel edge sloughs, over
Page 305 and 306:
Carbaryl can also be applied at 8 l
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habitat had a downwind width of 10
Page 309 and 310:
Depth of aquatic habitat (meters) B
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monitored in California, Idaho, Ore
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5.2 μg/L for carbofuran, 0.0150 -
Page 315 and 316:
Summary information for carbaryl, c
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after flooding (Nicosia, Carr et al
Page 319 and 320:
pesticide concentrations in the dis
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flowing water habitats, it is not s
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egistered products that contain mor
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potential ingredients in tank mixtu
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low maximum application rate. Howev
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occupy shoreline habitats of only a
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vertebrates and invertebrates (Walk
Page 333 and 334:
Temperature and toxicity We found n
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exposure concentrations. Moreover,
Page 337 and 338:
Summary of Toxicity Information Pre
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at several times during an experime
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Table 64. Assessment endpoint toxic
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fish, number of eggs per mature fem
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varigatus), an estuarine species, b
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included a NOAEC of 9.8 μg/L and a
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730 μg/L for D. magna (freshwater
Page 351 and 352:
TEP) are contained in Appendix D-1.
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the uncertainties related to experi
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capacity (Little and Finger 1990).
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consumed relative to unexposed fish
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24 hr exposure (Zinkl, Shea et al.
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We located studies that measured ol
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endpoints of salmonids remains a re
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items (Courtemanch and Gibbs 1980;
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single pulse of chlorpyrifos was in
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Table 65. Study designs and results
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Chemical Taxa/species Assessment me
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Chemical Taxa/species carbofuran ca
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Chemical Taxa/species carbofuran ca
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macroinvertebrate community did not
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Jardine, MacLatchy et al. 2005; Luo
Page 381 and 382:
Risk Characterization In this secti
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survival appears to be the most sen
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factor in the degree of toxicity of
Page 387 and 388:
Figure 41. Methomyl exposure concen
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Table 67. . Examples of published f
Page 391 and 392:
Additionally, the macroinvertebrate
Page 393 and 394:
Measured Concentrations in Willapa
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up to 100 m off the carbaryl applic
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average initial concentration from
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• Unrelated (0): Conclusive evide
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the fish to determine the cause of
Page 403 and 404:
Dose-addition assumes the cumulativ
Page 405 and 406:
Table 73. Predicted AChE inhibition
Page 407 and 408:
habitats during aerial applications
Page 409 and 410:
The second line of evidence is whet
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D. Impair swimming which leads to r
Page 413 and 414:
F. Exposure to mixtures of carbaryl
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used surfactant/adjuvant mixed with
Page 417 and 418:
In a second modeling exercise, we t
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Carbaryl’s thresholds for the fou
Page 421 and 422:
Table 75. Modeled output for Stream
Page 423 and 424:
Table 77. Modeled output for Sockey
Page 425 and 426:
The likelihood of scenarios 2 and 3
Page 427 and 428:
The three insecticides are highly t
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A. B. C. Figure 43. Probability plo
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elatively low survival EC50 values
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dominated by agricultural or urban
Page 435 and 436:
Figure 45. Percent change in lambda
Page 437 and 438:
Table 80. Multiple application scen
Page 439 and 440:
Because olfaction plays an importan
Page 441 and 442:
expect co-occurrence of the three i
Page 443 and 444:
support one or more lifestages. For
Page 445 and 446:
We attempted to compare expected co
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Cumulative Effects Cumulative effec
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entry into freshwater systems. Carb
Page 451 and 452:
Integration and Synthesis The Integ
Page 453 and 454:
carbofuran applications could cause
Page 455 and 456:
The Status of Listed Resources and
Page 457 and 458:
also exposed to poor water quality
Page 459 and 460:
Given the life history of LCR Chino
Page 461 and 462:
Chinook salmon. Furthermore, there
Page 463 and 464:
all three a.i.s are expected to be
Page 465 and 466:
completing migration to the Pacific
Page 467 and 468:
The major threats to this ESU ident
Page 469 and 470:
Land use data indicate that the Col
Page 471 and 472:
Central California Coast Coho Salmo
Page 473 and 474:
Pesticide use and detections in LCR
Page 475 and 476:
effects. In several streams, one or
Page 477 and 478:
ESU is evergreen forest. Between 19
Page 479 and 480:
miles where agricultural crops are
Page 481 and 482:
The Status of Listed Resources and
Page 483 and 484:
carbofuran application to potatoes,
Page 485 and 486:
The major threats to this DPS ident
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lowland areas (below 1,000 ft eleva
Page 489 and 490:
consequences and subsequent populat
Page 491 and 492:
and surface waters within the heavi
Page 493 and 494:
1994). Most juvenile steelhead spen
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salmon, Northern California steelhe
Page 497 and 498:
natural cover such as submerged and
Page 499 and 500:
The precise change in the conservat
Page 501 and 502:
coho salmon, LCR coho salmon, South
Page 503 and 504:
Table 81. Jeopardy and Non-Jeopardy
Page 505 and 506:
Reasonable and Prudent Alternatives
Page 507 and 508:
The RPA is comprised of six require
Page 509 and 510:
Table 83. Mandatory pesticide no ap
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items will die from these exposures
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action will attain this level in th
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proposed action. Therefore, inciden
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1. Minimize the amount and extent o
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met within the next 15 years, then
Page 521 and 522:
Arunachalam, S., K. Jeyalakshmi, et
Page 523 and 524:
Bortleson, G. C. and J. C. Ebbert (
Page 525 and 526:
CDFG (1995). "Letter dated 30 March
Page 527 and 528:
Davies, P. E. and L. S. J. Cook (19
Page 529 and 530:
FCRPS (2008). "Endangered Species A
Page 531 and 532:
Haggerty, M. J., A. C. Ritchie, et
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IEPSPWT (1999). "Monitoring, assess
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government from 1896 to 1945." Repo
Page 537 and 538:
Matthews, G. M. and R. S. Waples (1
Page 539 and 540:
NMFS (2004). Five-year integrated p
Page 541 and 542:
PSAT (2004). "State of the Sound 20
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Schroder, S. L. (1977). "Assessment
Page 545 and 546:
Tufts, D. F. (1990). "Control of bu
Page 547 and 548:
Williams, A. K. and C. R. Sova (196
Page 549 and 550:
Introduction To assess the potentia
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ocean-type and stream-type Chinook
Page 553 and 554:
incorporates empirical data when av
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given a percentile value of 50 (i.e
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species-appropriate growth period (
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For Figure 3C, an exposure pulse wo
Page 561 and 562:
the n x n square matrix (A) by assi
Page 563 and 564:
spawn (Pess et al. 2002). Survival
Page 565 and 566:
distributed survival and reproducti
Page 567 and 568:
Figure 1: Life-History Graphs and T
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Table 1. List of values used for co
Page 571 and 572:
Table 4. Matrix transition element
Page 573 and 574:
Figure 2. 555
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Figure 4. 557
Page 577 and 578:
Brewer, S.K., Little, E.E., DeLonay
Page 579 and 580:
Higgs, D.A., MacDonald, J.S., Levin
Page 581 and 582:
Morgan, M.J., and Kiceniuk, J.W. 19
Page 583 and 584:
Scholz, N.L., Truelove, N.K., Frenc
Page 585 and 586:
Appendix 2. Species and Population
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Chinook Salmon (continued) ESU Popu
Page 589 and 590:
Chum Salmon ESU Population λ - H=0
Page 591 and 592:
Coho Salmon (continued) ESU Populat
Page 593 and 594:
Steelhead (continued) DPS Populatio
Page 595 and 596:
Appendix 3: Abbreviations 7-DADMax
Page 597 and 598:
FQPA Food Quality Protection Act ft
Page 599 and 600:
PPE Personal Protection Equipment P
Page 601 and 602:
Appendix 4: Glossary 303(d) waters
Page 603 and 604:
Salmon fall to head upriver to its
Page 605 and 606:
Main channel The stream channel tha
Page 607 and 608:
Smolt A juvenile salmon or steelhea
Page 609:
WQS “A water quality standard def
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