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OREGON HOPS

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The field used to represent hop production in Oregon is located in Marion County, in the Willamette Valley. According to the 1997 Census of Agriculture, Oregon is ranked 2nd in hop production in the U.S. Marion County leads Oregon in acres planted in 1997. Hops require a rich organic soil, and abundant irrigation for maximum yield. The crop is perennial, old "bines" and other debris are removed in the spring and cultivated until late June or early July. Irrigation begins in May or early June. Harvest occurs from August to mid-September. Row widths vary from about 36 inches to more than 48 inches. The soil selected to simulate the field is a benchmark soil, Woodburn silt loam. Woodburn silt loam, is a fine-silty mixed, superactive, mesic Aquultic Agrixerolls. The series is used to produce berries, orchards, cannery crops, grain, hay, and pasture. Woodburn silt loam is a very deep, moderately well drained, slowly permeable soil with slow to medium runoff. These soils formed in stratified glacio lacustrine deposits of the Pleistocene age. They are found on nearly level to gently sloping broad valley terraces at elevations of 150 to 400 feet above mean sea level on slopes of 0 to 55 percent. The series is extensive in the Willamette Valley. Woodburn silt loam is a Hydrologic Group C soil.

Table 1.
PRZM 3.12 Climate and Time Parameters for Marion County Oregon - Hops
ParameterValueSource
Starting Date January 1, 1948Meteorological File - Salem, OR (W24232)
Ending Date December 31, 1983Meteorological File - Salem, OR (W24232)
Pan Evaporation Factor (PFAC) 0.73PRZM Manual Figure 5.1 (EPA, 1998)
Snowmelt Factor (SFAC) 0.16 cm C- 1PRZM Manual Table 5.1 (EPA, 1998)
Minimum Depth of Evaporation (ANETD) 17.0 cmPRZM Manual Figure 5.2 (EPA, 1998)

Table 2.
PRZM 3.12 Erosion and Landscape Parameters for Marion County Oregon - Hops
ParameterValueSource
Method to Calculate Erosion (ERFLAG) 4 (MUSS)PRZM Manual (EPA, 1998)
USLE K Factor (USLEK) 0.32 tons EI-1* GLEAMS Manual, Table of Representative Soils (USDA, 1985)
USLE LS Factor (USLELS) 0.945GLEAMS Manual, Table of Representative Soils (USDA, 1985)
USLE P Factor (USLEP) 1.0Set according to guidance (EPA, 2001)
Field Area (AFIELD) 172 haArea of Shipman Reservoir watershed (EPA, 1999)
NRCS Hyetograph (IREG) 2PRZM Manual Figure 5.12 (EPA, 1998)
Slope (SLP) 5%GLEAMS Manual, Table of Representative Soils; (USDA, 1985)
Hydraulic Length (HL) 600 mShipman Reservoir (EPA, 1999)

* EI = 100 ft-tons * in/ acre*hr


Table 3.
PRZM 3.12 Crop Parameters for Marion County, Oregon - Hops
ParameterValueSource
Initial Crop (INICRP) 1Set to one for all crops (EPA, 2001)
Initial Surface Condition (ISCOND) 1Set to residue prior to new crop planting
Number of Different Crops (NDC) 1Set to crops in simulation - generally one
Number of Cropping Periods (NCPDS) 36Set to weather data. Salem, OR (W24232)
Maximum rainfall interception storage of crop (CINTCP) 0.1PRZM Manual, Table 5.4 (EPA, 1998)
Maximum Active Root Depth (AMXDR) 203 cmSet to profile maximum. Roots can be as deep as 12 feet (EPA, 2001)
Maximum Canopy Coverage (COVMAX) 90Professional Estimate based on photography/video
Soil Surface Condition After Harvest (ICNAH) 3Continuous cultivation
Date of Crop Emergence
(EMD, EMM, IYREM)
30/03 http://www.oregon.gov/ODA/ Exit EPA Disclaimer
Date of Crop Maturity
(MAD, MAM, IYRMAT)
30/07
Date of Crop Harvest
(HAD, HAM, IYRHAR)
01/09
Maximum Dry Weight (WFMAX) 0.0Set to "0" Not used in simulation
SCS Curve Number (CN) 84, 79, 82Gleams Manual Table A.3,Meadow, condition good. (USDA, 1990)
Manning's N Value (MNGN) 0.023RUSLE Project, A12GCGCM Grapes Alleyway, Mulch Tillage (USDA, 2000)
USLE C Factor (USLEC) 0.294 - 0.522 RUSLE Project; A12GCGCM Grapes Alleyway, Mulch Tillage (USDA, 2000)

Table 4.
PRZM 3.12 Woodburn Soil Parameters for Marion County, Oregon - Hops
ParameterValue Verification Source
Total Soil Depth (CORED) 203 cm NRCS, National Soils Characterization Database (NRCS, 2001)
Number of Horizons (NHORIZ) 7 (Top horizon split in two)
First, Second, Third, Fourth, Fifth, Sixth, and Seventh Soil Horizons (HORIZN = 1,2,3,4,5,6,7)
Horizon Thickness (THKNS)
  • 10 cm (HORIZN = 1)
  • 13 cm (HORIZN = 2)
  • 20 cm (HORIZN = 3)
  • 40 cm (HORIZN = 4,6)
  • 50 cm (HORIZN = 2)
  • 30 cm (HORIZN = 7)
NRCS, National Soils Characterization Database (NRCS, 2001) http://soils.usda.gov/survey/nscd/ Exit EPA Disclaimer
Bulk Density (BD)
  • 1.44 g cm-3 (HORIZN = 1,2,5)
  • 1.53 g cm-3 (HORIZN = 3)
  • 1.45 g cm-3 (HORIZN = 4)
  • 1.37 g cm-3 (HORIZN = 6,7)
Initial Water Content (THETO)
  • 0.301 cm3-H2O cm3-soil (HORIZN =1,2)
  • 0.350 cm3-H2O cm3-soil (HORIZN =3)
  • 0.388 cm3-H2O cm3-soil (HORIZN =4)
  • 0.394 cm3-H2O cm3-soil (HORIZN =5)
  • 0.418 cm3-H2O cm3-soil (HORIZN =6)
  • 0.404 cm3-H2O cm3-soil (HORIZN =7)
Compartment Thickness (DPN)
  • 0.1 cm (HORIZN = 1)
  • 1.0 cm (HORIZN = 2)
  • 2.0 cm (HORIZN = 3,4)
  • 5.0 cm (HORIZN = 5,6)
  • 10.0 cm (HORIZN = 7)
Field Capacity (THEFC)
  • 0.301 cm3-H2O cm3-soil (HORIZN =1,2)
  • 0.350 cm3-H2O cm3-soil (HORIZN =3)
  • 0.388 cm3-H2O cm3-soil (HORIZN =4)
  • 0.394 cm3-H2O cm3-soil (HORIZN =5)
  • 0.418 cm3-H2O cm3-soil (HORIZN =6)
  • 0.404 cm3-H2O cm3-soil (HORIZN =7)
Wilting Point (THEWP)
  • 0.134 cm3-H2O cm3-soil (HORIZN = 1,2)
  • 0.153 cm3-H2O cm3-soil (HORIZN = 3)
  • 0.177 cm3-H2O cm3-soil (HORIZN = 4)
  • 0.185 cm3-H2O cm3-soil (HORIZN = 5)
  • 0.173 cm3-H2O cm3-soil (HORIZN = 6)
  • 0.156 cm3-H2O cm3-soil (HORIZN = 7)
Organic Carbon Content (OC)
  • 1.86% (HORIZN = 1,2)
  • 0.56% (HORIZN = 3)
  • 0.3% (HORIZN = 4)
  • 0.112% (HORIZN = 5)
  • 0.07% (HORIZN = 6)
  • 0.06% (HORIZN = 7)

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).

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