fferent irrigation sources. In this study, irrigation with raw
municipal sewage effluent produced the largest plants (height:
88.33 ±3.06 cm, collar diameter: 5.28 ±0.12 cm, and panicle
length: 9.10 ± 2.0 cm). Plants irrigated with raw sewage effluent
had 19 greater height, 5 greater collar diameter, and 25 greater
panicle length compared to those irrigated with well water.
Among the spray treatments, the least growth was observed
in the plants sprayed with tap water. The combination of Mn
and Zn in a foliar spray contributed to a greater plant growth
compared to the other spray treatment. The greatest growth
parameters (height: 84.00 ± 6.14 cm, collar diameter:
5.20 ±0.32 cm, and panicle length: 8.53± 0.70) were obtained
with a Mn and Zn foliar spray, whereas the lowest
(height: 74.08 ± 2.57 cm, collar diameter: 4.71 ± 0.15 cm,
and panicle length: 7.30± 0.30) growth parameters were obtained
with the control (tap water spraying).
Significant interaction between irrigation water sources and
micronutrient spraying was observed on the vegetative growth
parameters (Table 3). In the partition of this interaction, it was
evident that plants irrigated with raw or 50 diluted sewage
effluent had significantly higher growth rates within the Mn,
Zn, and Mn and Zn foliar applications compared to those irrigated
with well water.
fferent irrigation sources. In this study, irrigation with raw
municipal sewage effluent produced the largest plants (height:
88.33 ±3.06 cm, collar diameter: 5.28 ±0.12 cm, and panicle
length: 9.10 ± 2.0 cm). Plants irrigated with raw sewage effluent
had 19 greater height, 5 greater collar diameter, and 25 greater
panicle length compared to those irrigated with well water.
Among the spray treatments, the least growth was observed
in the plants sprayed with tap water. The combination of Mn
and Zn in a foliar spray contributed to a greater plant growth
compared to the other spray treatment. The greatest growth
parameters (height: 84.00 ± 6.14 cm, collar diameter:
5.20 ±0.32 cm, and panicle length: 8.53± 0.70) were obtained
with a Mn and Zn foliar spray, whereas the lowest
(height: 74.08 ± 2.57 cm, collar diameter: 4.71 ± 0.15 cm,
and panicle length: 7.30± 0.30) growth parameters were obtained
with the control (tap water spraying).
Significant interaction between irrigation water sources and
micronutrient spraying was observed on the vegetative growth
parameters (Table 3). In the partition of this interaction, it was
evident that plants irrigated with raw or 50 diluted sewage
effluent had significantly higher growth rates within the Mn,
Zn, and Mn and Zn foliar applications compared to those irrigated
with well water.
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