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Proceeding Paper

Effect of Phosphogypsum on Faba Bean Yield and Heavy Metals Content under Saline Conditions †

1
Agricultural Innovation and Technology Transfer Center (AITTC), Mohammed VI Polytechnic University (UM6P), Benguerir 43150, Morocco
2
Cherifian Phosphates Office (OCP), OCP sustainability platform, Casablanca 20200, Morocco
*
Author to whom correspondence should be addressed.
Presented at the 2nd International Laayoune Forum on Biosaline Agriculture, 14–16 June 2022; Available online: https://lafoba2.sciforum.net/.
Environ. Sci. Proc. 2022, 16(1), 16; https://doi.org/10.3390/environsciproc2022016016
Published: 16 June 2022
(This article belongs to the Proceedings of The 2nd International Laayoune Forum on Biosaline Agriculture)

Abstract

:
Salinity is one of the most severe abiotic stresses which causes significant losses to agricultural production, especially in arid and semi-arid areas. In the present study, we conducted a pots experiment to evaluate Phosphogypsum (PG) and Gypsum (G) as amendments and their effect on faba bean shoot and grain yield under saline conditions (soil ECe = 11.17 mS/cm, water EC = 1.5 mS/cm and water SAR = 4.2 meq/L). In addition, we investigated the safety of their application based on heavy metals content in the harvested grain. Our findings demonstrate that the use of PG as amendment for saline soil reclamation improved faba bean grain and biomass yield without affecting grain quality regarding heavy metal content.

1. Introduction

Salinity is one of the main challenges facing agricultural production systems in arid and semi-arid regions. Currently, the total land area impacted by high salt levels is about 1 billion hectares, and the area of affected land is significantly increasing [1]. In Morocco, the total soil affected by salinity is about 1.148 Mha [2].
Salt-affected soils usually generate physical and chemical disorders in soil–plant water systems. The reclamation of salt-affected soils can be done using several amendments, such as phosphogypsum, a byproduct of the phosphate industry. It was reported that PG effectively mitigates soil salinity and enhances crop yields [3].
The phosphate industry in Morocco, a major phosphate-based fertilizer producer, generates around 25 Mt of PG annually [4]. However, studies on the valorization of PG as a soil amendment in salt-affected soils in Morocco are scarce. The objectives of this study were to investigate the effect of the PG on faba bean shoot and grain yield and to investigate the safety of its application based on heavy metals content in the harvested grain under saline conditions.

2. Material and Methods

2.1. Soil Sampling and Analysis

Soil from the Sidi Elmokhtar region of Morocco was identified from a soil database and then sampled, air-dried and ground to pass through a 2 mm mesh sieve. Soil pH was measured in 1:5 soil:water extract. ECe is the electrical conductivity of saturated paste which was prepared by hand mixing [5]. The available phosphorus was determined using the Olsen method [6]. Spectrophotometry (Cary 60 UV–Vis, Agilent Technologies, Santa Clara, CA, USA) was used to determine sulfate, ammonium, chlorine and nitrate contents. The exchangeable sodium, potassium, calcium and magnesium were determined by atomic absorption spectroscopy (200 Series AA, Agilent Technologies, Santa Clara, CA, USA). The soil is saline, Table 1 shows the chemical properties of the soil.

2.2. Irrigation Water

pH and Ec were measured directly by a pH meter (InoLab pH 7310) and a conductometer (Mettler Toledo. SevenCompact). The sulfate, ammonium, chlorine and nitrate contents were quantified by spectrophotometry (Agilent Technologies. Cary 60 UV–Vis). The phosphorus, sodium, potassium, calcium and magnesium were determined by ICP (Agilent Technologies. 5110 ICP-OES). The water had a moderate salinity (Table 2).

2.3. PG and G Analysis and Pot Preparation

The experiment was conducted in pots in a greenhouse at Mohammed VI Polytechnic University in Benguerir, Morocco. Each pot was filled with 10 kg of soil. The PG used is that of Jorf Lasfar Phosphate, situated near the city of El Jadida. The second amendment was natural gypsum for agricultural use. PG and G were incorporated with the top 9 cm. The treatments consisted of: Control, 15 t/h of G, 15, 30 and 45 t/ha of PG. pH and EC were measured in a ratio of 1:5 PG or G:water extract. The rest of the elements were quantified by ICP-OES. PG is more acidic than G, and it is richer in nutrients (Ca, S and P). The chemical compositions of PG and G are presented in Table 3.

2.4. Statistical Analysis

Data were subjected to statistical analyses using IMB SPSS 20 software. One-way ANOVA tests were performed to test the difference between treatments. When ANOVA was significant, Tukey’s test was used to compare the means.

3. Results and Discussion

3.1. Yield Parameters

The amendments (G and PG) were associated with an increased number of grains and shoot yield. In pots, compared to the control, 30 t/ha and 45 t/ha of PG increased shoot dry matter by 52% and 54%, respectively (Table 4). Similar results were reported by [7] in maize trials where 20 t/ha and 40 t/ha of PG increased dry matter by 45% and 69%, respectively. Fresh biomass, fresh grain and dry weight were improved only with the highest rates of PG (30 and 45 t/ha) (Figure 1 and Table 4). The application of 30 and 45 t/ha increased grain dry weight by 52% and 62%, respectively, when compared to the control. In previous works, 10t/ha of G was enough to significantly increase faba bean grain yield [8]. PG application increased the yield of spring chickpeas by 50% and lentils by 27% [9]. The application of 30 and 45 t/ha also significantly increased thousand grain weight. However, neither PG nor G had a significant effect on the harvest index (Table 4).
Yield increases observed with PG compared to G may have been due to PG acidity and its calcium, sulfur and phosphor contents. In addition, PG was reported to dissolve faster and produce an acidic reaction in the rhizosphere, thus positively influencing nutrient availability [10].

3.2. Heavy Metals Content

This study showed that the application of the PG did not affect the grain quality. The grain heavy metals contents were below the recommended levels (Table 5) and were not affected by the application of PG and G. This finding is in agreement with a previous study where PG did not have an accumulative impact on plant heavy metal content [11]. This result can be explained by the alkaline soil pH as reported by [12] who indicated that transfer of heavy metals from soil to plants was negatively correlated with soil pH.

4. Conclusions

Results from this study have shown that the effectiveness of the treatments, on shoot and grain yield, was in the order of: 45 t/ha of PG > 30 t/ha of PG >15 t/ha of PG >15 t/ha of G > control. The application of 30 and 45 t/ha of PG increased grain dry weight by 52% and 62%, respectively, when compared to the control. Grain heavy metal contents were below the recommended limits and similar across treatments. Our findings suggest that the application of PG increased faba bean yield and can be considered as a safe amendment for reclaiming salt-affected soils.

Author Contributions

Conceptualization, K.E.M., M.E.G. and K.E.O.; methodology, K.E.M. and M.B.O.; software, M.B.O.; validation, K.E.M. and M.E.G.; formal analysis, M.B.O.; investigation, M.B.O.; resources, K.E.M., M.E.G. and K.E.O.; data curation, K.E.M.; writing—original draft preparation, M.B.O.; writing—review and editing, K.E.M.; visualization, M.B.O.; supervision, K.E.M. and M.E.G.; project administration, K.E.M., M.E.G. and K.E.O.; funding acquisition, K.E.O. All authors have read and agreed to the published version of the manuscript.

Funding

This research was financially supported by OCP sustainability platform under the specific agreement “AS 49–P1”.

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

Not applicable.

Acknowledgments

The authors would like to gratefully acknowledge the AITTC Soil, Water and Plant Analysis Laboratory, the AITTC experimental farm for providing the facilities and OCP sustainability platform for financial support to carry out the present investigation.

Conflicts of Interest

The authors declare no conflict of interest.

References

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  3. Saadaoui, E.; Ghazel, E.N.; Ben Romdhane, C.; Massoudi, N. Phosphogypsum: Potential uses and problems—A review. Int. J. Environ. Stud. 2017, 74, 558–567. [Google Scholar] [CrossRef]
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Figure 1. Dry and fresh grain weight of faba bean (mean ± standard deviation). Same letters in a column series indicate no significant differences among treatments.
Figure 1. Dry and fresh grain weight of faba bean (mean ± standard deviation). Same letters in a column series indicate no significant differences among treatments.
Environsciproc 16 00016 g001
Table 1. Soil chemical properties.
Table 1. Soil chemical properties.
Property/ElementpHEce
(mS/cm)
P2O5
(mg/kg)
K2O
(mg/kg)
CaO
(mg/kg)
Na2O
(mg/kg)
MgO
(mg/kg)
SO4
(mg/kg)
NO3
(mg/kg)
NH4
(mg/kg)
Value8.111.176730879847591067321140.26.05
Table 2. Chemical properties of irrigation water.
Table 2. Chemical properties of irrigation water.
Property/ElementpHEc
(mS/cm)
SAR
(meq/l)
K
(mg/L)
Na
(mg/L)
Ca
(mg/L)
Mg
(mg/)
NH4
(mg/L)
Cl
(mg/L)
SO4
(mg/L)
NO3
(mg/L)
P2O5
(mg/L)
Value7.81.54.228.6214.684.966.80.04252.264.024.80.05
Table 3. Chemical composition of PG and G.
Table 3. Chemical composition of PG and G.
Property/ElementpHEC
(mS/cm)
Ca
(%)
S
(%)
P
(%)
K
(ppm)
Mg
(ppm)
Cd
(ppm)
Zn
(ppm)
Cu
(ppm)
Fe
(ppm)
Ni
(ppm)
Pb
(ppm)
Phosphogypsum5.82.426.023.70.8869.0259.04.78.52.6126.71.81.9
Gypsum8.122.322.813.10.02969.07587.0<0.0039.92.42606.44.21.4
Table 4. Yield parameters of faba bean (mean ± standard deviation). Means followed by the same letter within the same column are not significantly different.
Table 4. Yield parameters of faba bean (mean ± standard deviation). Means followed by the same letter within the same column are not significantly different.
TreatmentsNumber of Grains (m2)Plant Fresh Weight (g/m2)Plant Dry Weight (g/m2)Thousand Grain Weight (g)Harvest Index (%)
Control106 ± 7 c464 ± 34 b198 ± 14 c1073 ± 71 b37% ± 1% a
15 t/h of Gypsum118 ± 7 bc504 ± 23 b227 ± 7 b1070 ± 50 b36% ± 2% a
15 t/h of Phosphogypsum118 ± 7 bc506 ± 13 b225 ± 8 b1152 ± 68 ab38% ± 2% a
30 t/h of Phosphogypsum140 ± 13 ab628 ± 24 a300 ± 11 a1236 ± 38 a37% ± 2% a
45 t/h of Phosphogypsum153 ± 18 a634 ± 14 a305 ± 12 a1215 ± 62 a38% ± 1% a
Table 5. Grain heavy metals content (mean ± standard deviation). Means followed by the same letter within the same column are not significantly different.
Table 5. Grain heavy metals content (mean ± standard deviation). Means followed by the same letter within the same column are not significantly different.
TreatmentsCuFeZnNiPbCd
ppm
Control12.7 ± 1.5 a62.7 ± 16.3 a72.7 ± 12 a3.4 ± 0.3 a<0.01<0.003
15 t/h of Gypsum11.2 ± 1.7 a85.2 ± 19.9 a67.2 ± 7.8 a3.6 ± 0.9 a<0.01<0.003
15 t/h of Phosphogypsum11.3 ± 2.3 a74.2 ± 28.8 a69.2 ± 8.5 a3.0 ± 0.3 a<0.01<0.003
30 t/h of Phosphogypsum12.0 ± 1.5 a78.7 ± 26.0 a82.2 ± 21.7 a3.0 ± 0.3 a<0.01<0.003
45 t/h of Phosphogypsum11.2 ± 1.7 a79.7 ± 20.8 a70.2 ± 6.6 a3.0 ± 0.2 a<0.01<0.003
Recommended Limits [13]73.3425.599.467.90.30.2
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MDPI and ACS Style

Outbakat, M.B.; El Gharous, M.; El Omari, K.; El Mejahed, K. Effect of Phosphogypsum on Faba Bean Yield and Heavy Metals Content under Saline Conditions. Environ. Sci. Proc. 2022, 16, 16. https://doi.org/10.3390/environsciproc2022016016

AMA Style

Outbakat MB, El Gharous M, El Omari K, El Mejahed K. Effect of Phosphogypsum on Faba Bean Yield and Heavy Metals Content under Saline Conditions. Environmental Sciences Proceedings. 2022; 16(1):16. https://doi.org/10.3390/environsciproc2022016016

Chicago/Turabian Style

Outbakat, M Barka, Mohamed El Gharous, Kamal El Omari, and Khalil El Mejahed. 2022. "Effect of Phosphogypsum on Faba Bean Yield and Heavy Metals Content under Saline Conditions" Environmental Sciences Proceedings 16, no. 1: 16. https://doi.org/10.3390/environsciproc2022016016

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