Abstract:The present study aimed to evaluate the agronomic performance of the sunflower crop irrigated with treated domestic wastewater and normal water (well-water) in a inceptisol of Apodi, State of Rio Grande do Norte, Brazil. The experiment was conducted in a randomized block experimental design, consisting of five treatments and five replications, using the H-251 sunflower cultivar from Embrapa. The treatments consisted of the application of five proportions of wastewater/well-water (T1-100% wastewater; T2-75% was… Show more
“…The highest Ni contents were found for T5 (only TOPW) in both soil layers, and the lowest was found for T1 (only underground water) in the soil surface layer ( Figure 2B). Costa (2018) found different results, with higher Ni contents in the soil surface layer when irrigated only with underground water (control). The mean Ni contents in both layers were below the limit of 30 mg dm -3 , which was established by the CONAMA (Resolution no.…”
Section: Dmentioning
confidence: 94%
“…The treatments followed the recommendations for wastewater dilution in underground water proposed by Costa et al (2018) to minimize risks of soil salinization and sodification.…”
The objective of this study was to evaluate changes in soil metal contents in an Ultisol cultivated with forage cactus (Nopalea cochenillifera) irrigated with diluted treated oil produced water (TOPW). The experiment was conducted in a randomized block design with five replications. The treatments consisted of 100% underground water (T1); 75% underground water plus 25% TOPW (T2); 50% underground water plus 50% TOPW (T3); 25% underground water plus 75% TOPW (T4); and 100% TOPW (T5). The plots consisted of 25 pots of 20 L in a greenhouse, in Mossoró, RN, Brazil. Soil samples from the 0-0.10 m and 0.10-0.20 m layers were collected at 240 days after planting, and Fe, Mn, Cu, Zn, Cr, Ni, Cd, and Pb contents were evaluated. The use of irrigations with diluted TOPW caused no contamination of the soils cultivated with forage cactus by the evaluated metals. T2 presented the lowest metal contents. Cr and Pb contents in the soil were significantly high, indicating that the application of TOPW should not be used continuously in the same area.
“…The highest Ni contents were found for T5 (only TOPW) in both soil layers, and the lowest was found for T1 (only underground water) in the soil surface layer ( Figure 2B). Costa (2018) found different results, with higher Ni contents in the soil surface layer when irrigated only with underground water (control). The mean Ni contents in both layers were below the limit of 30 mg dm -3 , which was established by the CONAMA (Resolution no.…”
Section: Dmentioning
confidence: 94%
“…The treatments followed the recommendations for wastewater dilution in underground water proposed by Costa et al (2018) to minimize risks of soil salinization and sodification.…”
The objective of this study was to evaluate changes in soil metal contents in an Ultisol cultivated with forage cactus (Nopalea cochenillifera) irrigated with diluted treated oil produced water (TOPW). The experiment was conducted in a randomized block design with five replications. The treatments consisted of 100% underground water (T1); 75% underground water plus 25% TOPW (T2); 50% underground water plus 50% TOPW (T3); 25% underground water plus 75% TOPW (T4); and 100% TOPW (T5). The plots consisted of 25 pots of 20 L in a greenhouse, in Mossoró, RN, Brazil. Soil samples from the 0-0.10 m and 0.10-0.20 m layers were collected at 240 days after planting, and Fe, Mn, Cu, Zn, Cr, Ni, Cd, and Pb contents were evaluated. The use of irrigations with diluted TOPW caused no contamination of the soils cultivated with forage cactus by the evaluated metals. T2 presented the lowest metal contents. Cr and Pb contents in the soil were significantly high, indicating that the application of TOPW should not be used continuously in the same area.
“…Treatments followed recommendations by [12] for wastewater dilution in underground water to minimize salinization and sodification risks in the soil. The following treatments were assessed: a) T1 -100% of underground water (UW), control; b) T2 -75% UW and % of produced water treatment (PW); c) T3 -50% UW and 50% PW; d) T4 -25% UW and 75% PW; e) T5 -100% PW.…”
Section: Methodsmentioning
confidence: 99%
“…Tested contrasts were a) treatment T5 vs other treatments (T1, T2, T3 and T4); b) treatment T4 vs treatments T1, T2 and T3; c) treatment T3 vs treatments T1 and T2; d) treatment T2 vs treatment T1. The combination of contrasts with treatment averages was expressed as follows, according to [12]. C1 = 12 m1 + 12 m2 + 8 m3 +10 m4 -42 m5 C2 = 30 m1 + 30 m2 + 20 m3 -80 m4 C3 = 6 m1 + 6 m2 -12 m3 C4 = 6 m1 -6 m2…”
Irrigation effects of produced water treatment, diluted in underground water, were analyzed through the chemical characteristics of argisol with foraging palm. Assay was performed in a randomized block design (RBD), with five replications, in a subdivided split plot scheme. Splits comprised treatments T1 (100% underground water - UW, control), T2 (75% UW and 25% produced water treatment - PW), T3 (50% UW and 50% PW), T4 (25% UW and 75% PW) and T5 (100% PW), whilst sub splits comprised soil depths (0 - 0.10 m and 0.10 - 0.20 m). The results showed that irrigation with diluted treated water produced no risk of soil salinization. There was evidence of leaching of the mobile ions to the deeper layer of soil, especially sodium and magnesium. The highest risk of sodification was observed for soil irrigated only with groundwater (T1 - control treatment).
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