OREGON FILBERTS (HAZELNUTS)
The field used to represent filbert production in Oregon is located in Washington County, in the Willamette Valley. According to the 1997 Census of Agriculture, Oregon is the leading producer of filberts in the U.S. Washington County is the second highest producing county in Oregon. Trees seldom require irrigation. The floor of the groves are kept smooth to permit easy harvesting of the nuts that have fallen to the ground, which occurs from September through November. The soil selected to simulate the field is a Cornelius silt loam. Cornelius silt loam, is a fine-silty, mixed, superactive, mesic Mollic Fragixeralfs. The series is used to produce berries, orchards, small grain and seed crop, hay and pasture. Cornelius silt loam is a moderately deep, moderately well drained, moderately slowly permeable soil with slow to medium runoff. The soil has a fragipan at about 2 feet. These soils formed in silt loess-like materials over mixed, fine-silty old alluvium of mixed origin. They are found on gently sloping to rolling low hills ans steep hill slopes with convex, long slopes and ridgetops at elevation of 350 to 800 feet above mean sea level. Slopes range from 2 to 60 percent. The series is not very extensive. Cornelius silt loam is a Hydrologic Group C soil.
|Starting Date||January 1, 1948||Meteorological File - Salem, OR (W24232)|
|Ending Date||December 31, 1983||Meteorological File - Salem, OR (W24232)|
|Pan Evaporation Factor (PFAC)||0.74||PRZM Manual Figure 5.1 (EPA, 1998)|
|Snowmelt Factor (SFAC)||0.2 cm C- 1||PRZM Manual Table 5.1 (EPA, 1998)|
|Minimum Depth of Evaporation (ANETD)||17.0 cm||PRZM Manual Figure 5.2 (EPA, 1998)|
|Method to Calculate Erosion (ERFLAG)||4 (MUSS)||PRZM Manual (EPA, 1998)|
|USLE K Factor (USLEK)||0.33 tons EI-1*||Farm Manual, Table 3.1 (EPA, 1985)|
|USLE LS Factor (USLELS)||3.62||Haan and Barfield, 1978|
|USLE P Factor (USLEP)||1.0||Set according to guidance (EPA, 2001)|
|Field Area (AFIELD)||172 ha||Area of Shipman Reservoir watershed (EPA, 1999)|
|NRCS Hyetograph (IREG)||4||PRZM Manual Figure 5.12 (EPA, 1998)|
|Slope (SLP)||12%||Value set to maximum for crop (EPA, 2001)|
|Hydraulic Length (HL)||600 m||Shipman Reservoir (EPA, 1999)|
* EI = 100 ft-tons * in/ acre*hr
|Initial Crop (INICRP)||1||Set to one for all crops (EPA, 2001)|
|Initial Surface Condition (ISCOND)||3||Set to reside prior to new crop planting; forest floor or meadow.|
|Number of Different Crops (NDC)||1||Set to crops in simulation - generally one|
|Number of Cropping Periods (NCPDS)||36||Set to weather data. Salem, OR (W24232)|
|Maximum rainfall interception storage of crop (CINTCP)||0.25||Set to default for orchards (EPA, 2001)|
|Maximum Active Root Depth (AMXDR)||90 cm||Set to partial soil series profile depth based on root penetrating the fragipan. Roots may grow to as much as 20 feet.|
|Maximum Canopy Coverage (COVMAX)||75||Based on aerial photography|
|Soil Surface Condition After Harvest (ICNAH)||3||Orchards floor maintained similar to a meadow|
|Date of Crop Emergence
(EMD, EMM, IYREM)
|Date of Crop Maturity
(MAD, MAM, IYRMAT)
|Date of Crop Harvest
(HAD, HAM, IYRHAR)
|Maximum Dry Weight (WFMAX)||0.0||Set to "0" Not used in simulation|
|SCS Curve Number (CN)||84, 79, 82||Gleams Manual Table A.3, meadow; condition good (USDA, 1990)|
|Manning's N Value (MNGN)||0.040||RUSLE Project, A13OFOFN for orchards, no-till- Salem, OR (USDA, 2000)|
|USLE C Factor (USLEC)||0.005 - 0.034||RUSLE Project; A13OFOFN for orchards, no-till- Salem, OR (USDA, 2000)|
|Total Soil Depth (CORED)||148 cm||NRCS, National Soils Characterization Database (NRCS, 2001)|
|Number of Horizons (NHORIZ)||5|
|First, Second, Third, Fourth, and Fifth Soil Horizons (HORIZN = 1,2,3,4,5)|
|Horizon Thickness (THKNS)||
||NRCS, National Soils Characterization Database (NRCS, 2001) http://soils.usda.gov/survey/nscd/|
|Bulk Density (BD)||
|Initial Water Content (THETO)||
|Compartment Thickness (DPN)||
|Field Capacity (THEFC)||
|Wilting Point (THEWP)||
|Organic Carbon Content (OC)|
EPA. 1985. Field Agricultural Runoff Monitoring (FARM) Manual, (EPA/600/3-85/043) Environmental Research Laboratory, U.S. Environmental Protection Agency, Athens, GA.
EPA. 1998. Carsel, R.F., J.C. Imhoff, P.R. Hummel, J.M. Cheplick, and A.S. Donigian, Jr. PRZM-3, A Model for Predicting Pesticide and Nitrogen Fate in the Crop Root and Unsaturated Soil Zones: Users Manual for Release 3.0. National Exposure Research Laboratory, Office of Research and Development, U.S. Environmental Protection Agency, Athens, GA.
EPA. 1999. Jones, R.D., J. Breithaupt, J. Carleton, L. Libelo, J. Lin, R. Matzner, and R. Parker. Guidance for Use of the Index Reservoir in Drinking Water Exposure Assessments. Environmental Fate and Effects Division, Office of Pesticide Programs, U.S. Environmental Protection Agency, Washington. D.C.
EPA. 2001. Abel, S.A. Procedure for Conducting Quality Assurance and Quality Control of Existing and New PRZM Field and Orchard Crop Standard Scenarios. Environmental Fate and Effects Division, Office of Pesticide Programs, U.S. Environmental Protection Agency, Washington, D.C.
Haan, C.T. and B.J. Barfield. 1978. Hydrology and Sedimentology of Surface Mined Lands. Office of Continuing Education and Extension, College of Engineering, University of Kentucky, Lexington, Kentucky 40506. pp. 286.
USDA. 1990. Davis, F.M., R.A. Leonard, W.G. Knisel. GLEAMS User Manual, Version 1.8.55. USDA-ARS Southeast Watershed Research Laboratory, Tifton GA. SEWRL-030190FMD.
USDA. 2000. Revised Universal Soil Loss Equation (RUSLE) EPA Pesticide Project. U.S. Department of Agriculture, National Resources Conservation Service (NRCS) and Agricultural Research Service (ARS).