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Clinton C. Shock, Joe H. Hobson, Jennifer Banner,
Lamont D. Saunders, and Timothy D. Stieber
Malheur Experiment Station
Oregon State University
Ontario, Oregon, 1992
Introduction
The potential of mechanically applied straw mulch
to reduce nutrient, pesticide and sediment losses from furrow irrigated
onions and increase water use efficiency was evaluated on a Nyssa silt
loam with three percent slope. Nitrogen and phosphorus losses in the
runoff were of particular interest, both because of their economic
importance as farm inputs and their roles as environmental
contaminants. Measured losses of phosphorus included phosphate-P
dissolved in runoff water, phosphate-P present in the sediment, and
total P in the sediment. Measured nitrogen losses included ammonium and
nitrate in runoff and on the sediment and total reduced N in the
sediment.
Methods
Dai Maru onions were planted in 22-inch rows in Nyssa silt loam with 3 percent slope that had received 0, 100, or 400 lb phosphate/acre in the form of triple superphosphate. Treatments consisted of complete factorial of two wheat straw mulch rates (0 and 800 lb/acre) and three rates of applied phosphate. Straw mulch was applied to the bottom of irrigation furrows (furrow-mulching) using a Hobson Mechanical Straw Mulch Applicator. The site was located at the Malheur Experiment Station, OSU, Ontario, Oregon and followed exactly on top of identical phosphate and mechanical straw mulch treatments for potatoes in 1990. The top foot of surface soil contained 10.4 mg/g nitrate-N and 3.9 mg/g ammonium-N. Onions were sidedressed with 180 lb N/acre as sulfur coated urea.
Forty five percent of the straw was applied to
the furrow bottoms prior to the first irrigation and 55 percent of the
straw was applied after cultivations prior to the fifth irrigation.
Onions were thinned to one plant for every 2.5 inches of row.
Irrigation furrows were 235 feet long and all furrows of all plots
received 17 irrigations during the season, with water inflow in each
furrow set at 2 gallons/minute. Irrigation duration in furrows with and
without mulch was identical. Weeds and insects were controlled using
normal commercial onion production practices. All irrigation furrows
were front wheel tracks of a John Deere 2040 tractor.
Water and Sediment Measurement
Onset of inflow, outflow, and hourly measurements
of inflow, outflow, and sediment yield were recorded. For each water
outflow rate reading, a one liter sample was placed in an Imhoff cone
and allowed to settle for 15 minutes. Sediment content in the water, y
in g/l, was found to be related to the Imhoff cone reading after 15
minutes (x) by the equation
y = 1.015x
r2 = 0.98
p < 0.0001.
Composite water samples were collected in 5 gallon buckets to obtain sediment samples for nutrient analysis during the first six irrigations. Sediment was analyzed for nitrate-N, ammonium-N, total N, phosphate-P, and total P.
Total inflow, outflow, infiltration, and sediment loss were integrated from hourly measurements using LOTUS 1-2-3 software program Infilcal 4.0 (Shock and Shock).
During six irrigations, hourly inflow water samples and hourly outflow water samples were collected from every plot. The collection time of the water was recorded and composite water samples were made in proportion to the sample represented in the water inflow or outflow using InfilCal 4.0 (Shock and Shock). Composite water samples were analyzed for nitrate-N, ammonium-N, and phosphate-P.
Net nutrient losses were calculated by comparing
the nutrient content in inflow water with the nutrient content in the
outflow plus sediment. Average nutrient concentrations from the six
monitored irrigations were used to estimate the nutrient concentrations
in the eleven irrigations where no water or sediment samples were
collected for analyses.
Results and Discussion
During the first irrigation, greater lateral movement of water was visually evident into the onion beds. Splitting the application of straw mulch allowed cultivation for weed control. Pronounced differences in sediment yield continued throughout the season as evidenced by Imhoff cones with runoff and sediment from mulched and non-mulched furrows during the eighth irrigation. Mechanical furrow mulching decreased runoff, increased infiltration, increased irrigation efficiency, and decreased sediment yield (Table 1). Water infiltration in the drier plots without mulch exceeded the crop's evapotranspiration water requirement.
Applied phosphate sensitively increased onion yields in both mulched and non-mulched plots (Table 2). All of the yield increase due to phosphate occurred in the largest and most desirable market size bulbs.
Furrow mulching increased onion yield, onion market grade, and gross economic return (Table 3). Lower economic responses would be expected on a less erodible site.
Sediment, phosphorus, and nitrogen losses were particularly large for onions grown on this site. Sediment and nutrient losses may be very high without furrow-mulching because the onion plant presents little in the way of roots or leaves to interfere with erosive processes.
Straw mulch reduced the losses of dissolved and soluble phosphate-P from 17.3 to 2.5 lb phosphate per acre (Figure 4) and insoluble-P lost in the sediment from 313 to 15.4 lb phosphorus per acre.
Losses of nitrate-N, ammonium-N, and organic-N
were similarly reduced by furrow mulching (Figures 5
and 6).
Conclusions
1. Large losses of sediment, nitrogen, and phosphorus occurred with the production of onion under furrow irrigation on a three percent slope.
2. Splitting the application of straw mulch allowed cultivation for weed control.
3. Mechanically applied straw mulch at 800 lb/acre decreased sediment yield, nitrogen losses, and phosphorus losses by 94.6, 88.8, and 94.6 percent respectively.
4. Onion yield, market grade, and gross economic return increased both with straw mulch and triple superphosphate.
5. Most of the phosphorus lost was in the form of insoluble phosphorus in the sediment. Most of the nitrogen lost was in the form of soil organic material in the sediment.
6. Furrows with straw mulch had net accumulation (not a net loss) of
soluble forms of phosphate, nitrate, and ammonium while furrows without
straw mulch suffered net losses of soluble nutrients.
Figure 1. Cumulative sediment loss from furrow irrigated onion
grown on a Nyssa silt loam (3% slope) with strawed and non-strawed
furrows. Malheur Experiment Station, Oregon State University,
Ontario, Oregon, 1991.
Figure 2. Cumultive phosphorus loss from furrow irrigated onions grown
on a Nyssa silt loam (3% slope) with strawed or non-strawed
furrows. Malheur Experiment Station, Oregon State University,
Ontario, Oregon, 1991.
Figure 3. Cumultive nitrogen loss from furrow irrigated onions grown on
a Nyssa silt loam (3% slope) with strawed or non-strawed furrows.
Malheur Experiment Station, Oregon State University, Ontario, Oregon,
1991.
Figure 4. Partitioning of phosphorus lossed from non-strawed and
strawed furrows into phosphate-P dissolved in the outflow water and
soluble-P and insoluble-P in the sediment. Malheur Experiment
Station, Oregon State University, Ontario, Oregon, 1991.
Figure 5. Partitioning of nitrogen losses from non-strawed
furrows into ammonium-N and nitrate-N in the runoff water and
ammonium-N, nitrate, and organic-N in the sediment. Malheur
Experiment Station, Oregon State University, Ontario, Oregon, 1991.
Figure 6. Partitioning of nitrogen losses from strawed furrows
into ammonium-N and nitrate-N in the runoff water and ammonium-N,
nitrate, and organic-N in the sediment. Malheur Experiment
Station, Oregon State University, Ontario, Oregon, 1991.
Table 1. Total irrigation, runoff, irrigation efficiency, infiltration,
and sediment yield for a Nyssa silt loam with three percent slope
planted to onions. Malheur Experiment Station, Oregon State University,
Ontario, OR, 1991.
| Furrow mulching | |||
| None | Strawed | LSD(0.05) | |
| Water applied, ac-ft/ac | 8.3 | 8.2 | ns |
| Water runoff, ac-ft/ac | 6.2 | 3.6 | 5.1 |
| Irrigation efficiency, % | 24.9 | 57 | 5.1 |
| Water infiltration, ac-ft/ac | 2.1 | 4.7 | 6.4 |
| Sediment lost, tons/ac | 148.7 | 7.4 | 8.1 |
Table 2. Market grade and total yield of onions grown at three
phosphorus levels with and without furrow mulching. Malheur Experiment
Station, Oregon State University, Ontario, Oregon, 1991.
| Treatment | Yield by market grade | ||||||
| Furrow
Mulching |
Applied
P Kg/ha |
Small | Medium | Jumbo
< 4" |
Colossal | (All Jumbo) | Total |
| - - - - - - - - - - - - - - - - Mg/ha - - - - - - - - - - - - - - - - - | |||||||
| None | 0 | 3.5 | 25.9 | 9.3 | 0.8 | -10.1 | 39.5 |
| 49 | 2.7 | 22.9 | 12.3 | 0.6 | -12.9 | 38.5 | |
| 196 | 2.4 | 24.5 | 19.4 | 1.9 | -21.3 | 48.2 | |
| AV | 2.9 | 24.4 | 13.7 | 1.1 | -14.8 | 42.1 | |
| Strawed | 0 | 1.7 | 25.3 | 31.9 | 3.8 | -35.7 | 62.7 |
| 49 | 1.4 | 19.4 | 37.8 | 8.2 | -46 | 66.8 | |
| 196 | 1 | 15.3 | 46 | 15.1 | -61.1 | 77.4 | |
| AV | 1.4 | 20 | 38.6 | 9 | -47.6 | 69 | |
| LSD(0.05) Mul. | 0.5 | ns | 4.4 | 2.1 | -5.5 | 6.6 | |
| LSD(0.05) P level | 0.6 | ns | 5.3 | 2.5 | -6.7 | 9.1 | |
| LSD(0.05) M x P | ns | ns | ns | 3.6 | (ns) | ns | |
Table 3. Market grade, total yield, and gross economic
return of onions grown with and without furrow mulching. Oregon State
University, Malheur Experiment Station, Ontario, Oregon, 1991.
| Non-strawed | Strawed | |||||
| Market
class |
Bulb diameter | Yield | Gross revenue | Yield | Gross revenue | LSD
(0.05) |
| cwt/ac | $/ac | cwt/ac | $/ac | cwt/ac | ||
| Small | [ 2¼" | 25.8 | 0 | 12.3 | 0 | 4.7 |
| Medium | 2 ¼ to 3" | 218.2 | 218 | 178.5 | 179 | ns |
| Jumbo | 3 to 4" | 121.9 | 488 | 344.2 | 1,277 | 38.9 |
| Colossal | m 4" | 9.7 | 39 | 80.8 | 323 | 18.5 |
| (Jumbo & Colossal) | (m 3") | -131.6 | -425 | -49.2 | ||
| Cull disposal | -39 | -67 | ||||
| Total | 365.9 | 706 | 615.8 | 1,812 | 66.3 | |
Table 4. Accounting of phosphate-P, nitrate-N and
ammonium-N accumulations and losses in the water under furrow-mulched
onions.
| Irrigation water applied | Average nutrient concentration in irrigation water | Estimated nutrients applied in irrigation water | Average nutrient concentration in runoff water | Lost in runoff water plus sediment | Net Loss
or accumulation |
|||
| ac-ft/ac | ppm | lb/ac | ppm | kg/ha | lb/ac | |||
| Non-strawed furrows | ||||||||
| Phosphate-P | 8.3 | 0.15 | 3.3 | 0.43 | 17.3 | 14 | Loss | |
| Ammonium-N | 8.3 | 0.24 | 5.4 | 0.27 | 6.2 | 0.8 | Loss | |
| Nitrate-N | 8.3 | 1.78 | 39.9 | 1.67 | 34.1 | 5.8 | Loss | |
| Strawed furrows | ||||||||
| Phosphate-P | 8.2 | 0.15 | 3.3 | 0.22 | 2.5 | 0.8 | Acc | |
| Ammonium-N | 8.2 | 0.24 | 5.4 | 0.2 | 2.7 | 2.7 | Acc | |
| Nitrate-N | 8.2 | 1.78 | 39.9 | 1.51 | 19.8 | 20.1 | Acc | |
Malheur Agricultural Experiment
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