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Each plot consisted of eight alfalfa rows, 480 ft long, with two subplots corresponding to the two alfalfa varieties. Each plot was irrigated separately by its own pressure regulator, electronic solenoid valve, and water meter. Water meters were read before and after each irrigation.
Alfalfa Etc was calculated with a modified Penman equation (Wright 1982) and peak alfalfa crop coefficients using data collected at the Malheur Experiment Station by an AgriMet weather station (U.S. Bureau of Reclamation, Boise, ID) adjacent to the field. The Etc was estimated and recorded from dormancy break on March 10 until the final irrigation on August 18. After the alfalfa was flailed, the Etc was adjusted using crop coefficients. The crop coefficients were derived from weekly measurements of the percent ground cover until full cover was achieved.
Volumetric soil water content was determined by one Gro-Point soil moisture sensor (Environmental Sensors Inc., Escondido, CA) installed at 12-inch depth and one at 20-inch depth in each plot. The Gro-Point sensors were installed horizontally halfway between the drip tape and the alfalfa row in the plot center. Sensors were located 70 ft from the center of the field in the Tango subplots. Sensors were connected by buried cables to electronic communication boards housed in two locations in the field. The electronic communication boards were connected by a cable to a personal computer allowing the soil water content to be read and logged every hour.
On August 19, biomass samples were taken in each subplot by cutting the plants at ground level in 3.3 ft of one row. The samples were weighed, oven dried, and weighed again. The dried samples were separated into stems, leaves, and seed pods.
The alfalfa was desiccated with Boa (Paraquat dichloride) at 0.63 lb ai/acre and Reglone (Diquat) at 0.5 lb ai/acre on August 29. On September 12, 66 ft of each subplot was harvested with a small plot combine (52-inch width). The harvested seed was cleaned to separate the plant debris from the seed. The seed and the debris were weighed. A subsample of 2001 and 2002 seed from each plot was analyzed for quality by the Oregon State University Seed Laboratory on June 30, 2003. A 400-seed sample was taken from each subsample and analyzed for germination, hard seed, abnormal seed, and dead seed.
Lygus bugs were monitored twice weekly by taking three 180° sweeps with an insect net in each plot. The total number of early and late instars and adults was counted at each location. When the total number of insects (early and late instars, and adults) reached four per sweep, insecticides were applied (Table 1).
| Date | Product | Rate |
| lb ai/acre | ||
| June 11 | Capture | 0.1 |
| June 11 | Cygon | 0.5 |
| June 26 | Metasystox-R | 0.5 |
| July 16 | Dibrom | 0.9 |
| July 16 | Warrior | 0.02 |
| August 4 | Capture | 0.032 |
| August 8 | Dibrom | 1.4 |
| August 8 | Warrior | 0.03 |
The total Etc from dormancy break to the start of flowering (March 10 to June 6) was 11.4 inches, substantially higher than the approximately 4 inches applied uniformly to all plots (Fig. 1a). After the start of flowering, the treatments were clearly differentiated in terms of cumulative amount of water applied over time (Fig. 1b). The total amount of water applied after the start of flowering was 21.4, 16.2, 10.8, and 5.4 acre-inches per acre for treatments 1-4, respectively. The total Etc from the start of flowering until the last irrigation was 26.8 acre-inches. The total Etc for the season was 38.2 inches.
Soil moisture was closely related to the irrigation treatments (Fig. 2). The average soil moisture content at 12-inch depth from June 7 through August 20 was 31, 25, 23, and 20 percent for treatments 1-4, respectively. Soil moisture content at 12-inch depth for treatments 1-3 was similar during irrigations, but became lower between irrigations in accordance with the irrigation treatments. Soil moisture content at 12-inch depth for treatment 4 (irrigated at 20 percent Etc), remained lower than for the other treatments during and after irrigations. Soil moisture content at 20-inch depth was lower than at 12-inch depth for all treatments (Fig. 3). Soil moisture content at 20-inch depth for treatments 1-3 was similar during and between irrigations. Soil moisture content at 20-inch depth for treatment 4 did not respond to irrigations.
Alfalfa seed yield increased with increasing Etc replacement (Fig. 4) and applied water (Fig. 5), reached a maximum, and then decreased. Tango seed yield was highest at 67 percent of Etc replacement or 24.1 inches of applied water (total water applied from the start of the season) and Accord seed yield was highest at 64 percent of Etc replacement or 21.6 inches of applied water.
Each year, seed pod dry matter as a percentage of total plant dry matter increased with increasing Etc replacement, reached a maximum, and then decreased (Fig. 6). In 2003, seed pod dry matter was highest by 49 and 37 percent of Etc replacement for Tango and Accord, respectively (Table 3).
The Etc replacement that resulted in the highest seed yield increased over the years (Table 2). The Etc replacement that resulted in the highest seed pod dry matter was lower in 2001 than in 2002 or 2003. Seed pod dry matter was maximized by lower Etc replacement than seed yield in 2001 and 2003.
Germination decreased with increasing Etc replacement for the 2001 and 2002 seed (Fig. 7). Seed defects (hard seed, abnormal seed, and dead seed) also increased with increasing Etc replacement (Table 3).
Lygus bug insecticide applications were effective in maintaining the population below the economic threshold (four lygus bugs per 180° sweep) until around July 11 (Fig. 8).
| Tango | Accord | ||||||
Year |
Highest seed yield |
Etc replacement for highest seed yield |
Etc replacement for highest % seed pod dry matter | Highest seed yield |
Etc replacement for highest seed yield |
Etc replacement for highest % seed pod dry matter | |
| lb/acre | --------- % Etc --------- | lb/acre | -------- % Etc --------- | ||||
| 2001 | 643 | 39 | 32.7 | 736 | 45 | 20 | |
| 2002 | 449 | 51 | 49.3 | 533 | 50 | 47.4 | |
| 2003 | 251 | 67 | 48.7 | 303 | 64 | 37.2 | |
| Hard seed | Abnormal seed | Dead seed | |
| 2001 | |||
| 20 | 5.7 | 1.8 | 0.4 |
| 40 | 6.9 | 3.4 | 4.3 |
| 60 | 8.2 | 3 | 3.2 |
| 80 | 12.7 | 4.7 | 7.1 |
| LSD (0.05) | 5.5 | 2.2 | 4.1 |
| 2002 | |||
| 0 | 12.1 | 5.4 | 5.8 |
| 40 | 16.5 | 4.5 | 6.8 |
| 60 | 24.8 | 4.2 | 12.7 |
| 80 | 27.1 | 5.2 | 28.5 |
| LSD (0.05) | 6.9 | ns | 6.2 |





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