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Annals of Environmental Science and Ecology

Response of Rain-Fed Upland Rice (Oryza Sativa L.) to Different Rates of Nitrogen and Phosphorus Nutrients on Vertisols of North Western Amhara, Ethiopia

Abstract Abstract INTRODUCTION MATERIALS AND METHODS RESULTS AND DISCUSSION REFERENCES
Details

Received: 15-Dec-2025

Accepted: 03-Jan-2026

Published: 05-Jan-2026

Yohannes Kefale1*, Zenebe Gebremedhin2, Daniel Tadesse2 and Tamirat Worku1

1Amhara Agricultural Research Institute, Gondar Agricultural Research Center, Ethiopia

2College of Agriculture and Environmental Sciences, University of Gondar, Ethiopia

Corresponding Author:

Yohannes Kefale, Amhara Agricultural Research Institute, Gondar Agricultural Research Center, Ethiopia, Tel: 0918241756

Keywords

Nitrogen; Phosphorus; Upland Rice; Yield.

Abstract

A field experiment was carried out at Metema and Tach Armachiho districts of North Western Amhara to investigate the effect of nitrogen and phosphorous fertilizer rates on yield and yield components of upland rice during the main cropping season of 2020/2021. At both experimental sites, a factorial combination of four levels of nitrogen (0, 46, 92 and 138kg ha-1) and three level of P2 O5 (0, 23, 46 kg ha-1) were tested in randomized complete block design with three replications. A combined analysis of variance revealed highly significant (p<0.01) difference among the traits panicle length, number of effective tillers and grain yield for the interaction effect of Nitrogen and Phosphorus nutrients rates while thousand seed weight was significant (p<0.05). For other traits recorded, non-significant interaction effect was observed while significant for one or two of the nutrient rates applied. The combined application of 92 and 46 kg N - P2 O5 ha-1 gave yield of 6170 kg ha-1 which is higher than other fertilizer rate interactions. The partial budget analysis also indicated that the application of 92 and 46 kg N - P2O5 ha-1 had the highest net benefit (Birr 119,245.3 ha-1), with acceptable marginal rate of return (1151.48%) as compared to other treatments. Therefore, application of 92 kg N ha-1 and 46 kg P2 O5 ha-1 is recommended for upland rice growers in both Tach Armachiho and Metema areas and other similar agro-ecologies

Abstract

A field experiment was carried out at Metema and Tach Armachiho districts of North Western Amhara to investigate the effect of nitrogen and phosphorous fertilizer rates on yield and yield components of upland rice during the main cropping season of 2020/2021. At both experimental sites, a factorial combination of four levels of nitrogen (0, 46, 92 and 138kg ha-1) and three level of P2 O5 (0, 23, 46 kg ha-1) were tested in randomized complete block design with three replications. A combined analysis of variance revealed highly significant (p<0.01) difference among the traits panicle length, number of effective tillers and grain yield for the interaction effect of Nitrogen and Phosphorus nutrients rates while thousand seed weight was significant (p<0.05). For other traits recorded, non-significant interaction effect was observed while significant for one or two of the nutrient rates applied. The combined application of 92 and 46 kg N - P2 O5 ha-1 gave yield of 6170 kg ha-1 which is higher than other fertilizer rate interactions. The partial budget analysis also indicated that the application of 92 and 46 kg N - P2O5 ha-1 had the highest net benefit (Birr 119,245.3 ha-1), with acceptable marginal rate of return (1151.48%) as compared to other treatments. Therefore, application of 92 kg N ha-1 and 46 kg P2 O5 ha-1 is recommended for upland rice growers in both Tach Armachiho and Metema areas and other similar agro-ecologies.

INTRODUCTION

Rice (Oryza sativa L.) belongs to the family Poaceae; it is an essential food crop and a major food grain for more than half of the world’s population [1]. It is a cereal crop that has been gathered, consumed and cultivated by many people worldwide for more than 10,000 years, longer than any other crop [2]. To meet the food demand of an ever-increasing human population, the world’s rice grain production should be increased, while rice straw, after being chopped into fine parts, is used as animal feed. The global rice cultivation was estimated at total area 163 million ha with annual production averaging 730.2 million tons [3]. Rice production in Ethiopia has begun in recent years and is expected to grow. Although rice has been introduced to the country very recently, it is a productive crop next to maize in the country and is among the target commodities that have received due emphasis in the promotion of agricultural production by the government of Ethiopia to ensure household as well as national food security in the country [4].food crops, normally without any fertilizer used [5]. The major rice producing regions in the country are the Amhara, Oromia and South and Ethiopia regions with a share of 76%, 14.9%, and 5.2%, respectively [6]. Rice cultivation, however, continues on potential land in the country [7]. Currently, rice is showing an increasing trend in Ethiopia in terms of the area of production as it increased from 24,434 ha in 2000 to 57,575.72 ha in 2019 [8]. Despite the fact that rice was introduced to Ethiopia 50 years ago, its production and productivity remain low. The average national yield of rice is about 2.96 t ha-1 [8] which is lower compared to the world average productivity of 5.1 t ha-1. This low rice productivity in the country is associated with a lack of various N and P sources of fertilizer and improved rice varieties [9]. Poor soil fertility is among the major factors limiting rice production in Ethiopia. Nitrogen, phosphorus, and potassium are applied as fertilizers in large quantities to rice fields and a deficiency of either of the nutrients leads to yield losses [10]. Nitrogen and phosphorus is often cited as the most limiting nutrients in the agricultural soil of Ethiopia. Relatively, those nutrients are deficient in valleys where nitrogen is subjected to leaching, while the limited availability of phosphorus is observed due to several factors [11]. Even though determination of an appropriate dosage of application would be both economical and appropriate to enhance the productivity and consequent profit of the grower, there are no scientific findings for the determination of the optimum N and P fertilizer level in the study area. Therefore, the objective of the study was to develop optimum rates of nitrogen and phosphorous nutrients for upland rice (NERICA-4) which could be used to enhance rice production increment in Metema and Tach Armachiho districts.

MATERIALS AND METHODS

Description of the Study Area

Field experiment was conducted in Metema and Tach Armachiho districts during the main cropping season of 2020. These districts are located in the West Gondar Zone and Central Gondar of the Amhara national regional state, Ethiopia respectively. Metema district is 912 km from the capital city Addis Abeba and 200 km from Gondar and geographically located at 120 47’ Latitude to 38 027’ [12]. It is bounded by Sudan. The altitude of the Metema district ranges from 550 to 1608 meters above sea level (m.a.s.l). The mean maximum and minimum temperatures in the area are about 40.0 °C and 15.0°C, respectively. The mean annual rainfall in the area is about 650.5 mm and it is erratic and uneven in distribution. Tach Armachiho is located at latitude 130 19’ 60’’ and longitude 360 44’60’’. The district’s elevations range from 550 to 1600 meters. The mean maximum and minimum temperatures in the area are about 34.0°C and 13.0°C, respectively. The average annual rainfall in the area ranges between 600 and 605mm. In both districts, the rainy months extend from June until the end of September. However, most of the rainfall is received during July and August. The study area had a mono-modal rainfall characteristic. The location represents the major rice-producing agro ecology of the region. Some of the major crops grown in both districts include sorghum, sesame, cotton, soybeans and finger millet. Rice variety NERICA-4 was used for the experiment as it is high yielder variety and popular among the farmers in the study area.

Experimental Treatments, Design, Procedures and Trial Management

The treatments comprised factorial combinations of four levels of nitrogen (0, 46, 92, 138 kg N ha-1) and three levels of phosphorus (0, 23, 46 kg P2 O5 ha-1). Urea (46% N) and Triple Super Phosphate (46% P2 O5 ) were used as fertilizer sources for N and P2 O5 , respectively. A total of 12 treatment combinations was being studied in a randomized complete block design with three replications. The gross and net plot sizes were 3 m width and 3m length (9 m2) with 12 rows and 2.5 m width and 2.0 m length (5.0 m2) with 10 rows, respectively. The space between blocks, plots and row spacing was maintained at 1.5 m, 1m and 0.25 m, respectively. The date of planting was on July 2 and 3, 2020 for Tach Armachiho and Metema respectively, with a seed rate of 60 kg ha-1 at a depth of 3-5 cm. Except for the control plots, all phosphorus nutrient was applied at planting, while nitrogen was applied in splits. All other management practices were applied as per the general recommendations for rice. Initial soil samples were taken following the procedures of surface soil sampling at 0-30 cm soil depth from 5 random spots on the experimental site in a zigzag pattern by vertical insertion of the auger before planting. The samples were then air-dried, ground with a pestle and mortar, and passed through a 2 mm sieve to create a 1 kg composite sample that was labeled in plastic bags. The composite samples were taken to Gondar soil testing laboratories and Adet Research Center for selected physical and chemical properties, mainly soil texture (percent sand, silt and clay), soil pH, EC, CEC, total N, available P, Ca, K, Na, Mg, SOC and SOM. Data were collected on major agronomic and phenological characters. The collected data was subjected to analysis of variance (ANOVA) using SAS (9.0) and interpretations were drawn following the procedure described by Gomez AA [13]. Homogeneity of variances was tested using F test as described by Gomez AA [13]. According to the homogeneity test, all parameters were homogenous except days to maturity. Least significant differences (LSD) test at 1 and 5% level of probability was used. Correlation analysis was also done to examine the association between the yield and the yield-related components. The partial budget analysis as described by CIMMYT [14], was done to determine the economic feasibility.

RESULTS AND DISCUSSION

Soil Physical and Chemical Properties in the Study Areas

The soil analysis of the two sites indicated that the pH value of the soil was in the range of 6.7-7.2, which indicated that it was slightly acidic to neutral. It is suitable for rice production since rice grows well in heavy clay or clay loam soils. The texture of these soils is clay with low to moderate organic matter content and relatively easily weathering minerals (Table 1). The soil had low available phosphorus, which indicates that an additional P fertilizer is required for optimum crop growth and yield [15]. The result of the experimental area for total nitrogen was medium according to the rating of [16].

Days to 50% heading and days to 90% physiological maturity

The combined ANOVA indicated that the main effect of N and P rates and their interaction did not show significant difference on days to 50% heading and 90% days to maturity (Table 2).

Effect of Treatments on growth parameters of upland rice

Analysis of variance showed that the main effects of nitrogen (P<0.001) and phosphorous (P<0.01) fertilizer rates had significant on plant height and panicle length while their interaction had not been significant (P<0.05) on plant height but significant to panicle length (Table 2). Concerning the nitrogen rate, the tallest plant height (114.9 cm) was recorded at the highest nitrogen rate of 138 kg ha-1, while the shortest plant height (62.57 cm) was recorded at the control without N application (Table 6). In line with the present finding [17], reported that shorter plant height was noted at the control without N fertilizer application. With regard to phosphorous rate, the tallest rice plants (85.78 cm) were recorded at plots fertilized with 46 kg P2 O5 ha-1 while the shortest plants (79.9 cm) measured from the control without P application (Table 6). In line with the present results [18], and [19] reported significant effects of N application on plant height (Table 3&4). The longest panicle length (22.6cm) exhibited the interaction effects of 138kg ha-1 N and 46 kg of P2 O5 rates, while the shortest panicle length (14.5cm) was recorded from the control treatments (Table 7). In line with the findings of the present study [19]), reported that the application of nitrogen and phosphorus fertilizers significantly enhanced the growth of upland rice panicle length (Table 8).

Table 1: Selected soil physicochemical properties of the experimental site.

A. physical analysis

Locations

 

Metema

Tach Armachiho

 

Particulars

Value

Status

Value

Status

Method employed

Sand (%)

22

 

23

 

 

Silt (%)

27.72

 

26.5

 

 

 

Clay (%)

 

49.88

 

 

48.13

 

Bouyoucos hydrometer method

textural class

Clay

Clay

 

 

 

B. chemical analysis

 

 

 

 

 

pH (by 1: 2.5 soil water ratio)

 

6.7

 

Neutral

 

6.7

 

Neutral

 

1:2.5 water with pH meter

Organic Carbon (%)

2.31

Law

2.5

moderate

Walkley and Black

Total N (%)

0.15

Medium

0.16

Medium

Kjeldahl digestion &distillation

Available P (ppm)

2.67

Law

2.9

Low

Bray II

Organic Matter (%)

2.5

Law

2.7

Low

Walkley and Black

 

 

 

 

 

 

CEC (meq/100g soil)

69.07

Very high

74.9

Very high

Bremner and Mulvaney

EC (ms/cm

0.12

Low

0.12

Low

1:5 soil to water ratio suspension

Ca (cmol kg-1)

48.03

Very high

48.07

Very high

 

Mg (cmol kg-1)

17.01

Very high

18.01

Very high

 

K (cmol kg-1)

0.66

Very high

1.5

low

 

Na (cmol kg-1)

1.12

low

1.5

low

 

CEC=Cation Exchange Capacity, EC=electrical conductivity, ppm=Part per million.

Table 2: ANOVA for phenological and growth parameters of Upland rice as affected by rate of N and P2O5 applications at North Western Gondar, Ethiopia in 2020

Source

DF

DM

DH

PL

PH

Rep

2

10.74ns

0.78ns

1.19ns

37.94ns

N Rate

3

8.94ns

2.15ns

90.24***

5838.87***

P2O5

2

0.59ns

2.17ns

14.09**

184.27**

N Rate * P2O5

6

8.18ns

4.65ns

4.54*

68.89ns

Error

22

6.04

4.05

1.54

32.56

CV (%)

 

2.49

3.14

6.38

6.37

DF= degree of freedom; DM=days to maturity; DH= days to heading; PL=panicle length; PH=plant height; CV= Coefficient of Variation, ns, *, ** and *** = non-significant, significantly different at 5 %, 1% and 0.1%, respectively

Table 3: ANOVA for phonological and growth parameters of Upland rice as affected by rate of N and P2O5 applications at North Western Gondar, Ethiopia in 2020.

Source

DF

SPP

ET

NET

TT

Rep

2

0.82ns

2995.41ns

9367.1*

7729.89ns

N Rate

3

14.63***

9989.654**

3381.034ns

9938.1ns

P2O5

2

17.67***

3115.99ns

112.88ns

2678.56ns

N Rate * P2O5

6

1.30ns

6135.08*

3130.37ns

11747.1ns

Error

22

0.88

2174.9

2537.53

4693.02

CV (%)

 

8.48

20.76

46.3

20.55

DF= degree of freedom; SPP= Spikelet per panicle, ET= Effective tiller; NET=none effective tiller, TT=Total tiller; CV= Coefficient of Variation, ns, *, ** and

*** = non-significant, significantly different at 5 %, 1% and 0.1%, respectively

Table 4: ANOVA for phonological and growth parameters of Upland rice as affected by rate of N and P2O5 applications at North Western Gondar, Ethiopia in 2020

Source

DF

NFG

TSW

GY

BY

Rep

2

367.81ns

0.29ns

0.06ns

1.89ns

N Rate

3

1218.3***

13.64**

43.53***

204.61***

P2O5

2

333.813ns

5.67**

6.3947818***

8.65*

N Rate * P2O5

6

129.49ns

3.66*

0.51*

2.43ns

Error

22

139.1

0.80

0.19

2.45

CV (%)

 

12.3

3.27

10.73

18.36

DF= degree of freedom; NFG= number of filled grain, TSW= Thousand seed weight; GY=Grain yield, BY=Biomass yield; CV= Coefficient of Variation, ns, *, ** and *** = non-significant, significantly different at 5 %, 1% and 0.1%, respectively

Table 5: ANOVA for phonological and growth parameters of Upland rice as affected by rate of N and P2O5 applications at North Western Gondar, Ethiopia in 2020

Source

DF

STY

HI

Rep

2

1.76ns

0.0075486ns

N Rate

3

59.48***

0.0027 ns

P2O5

2

0.25ns

0 0.0249*

N Rate * P2O5

6

0.89ns

0.002585ns

Error

22

1.85

0.078

CV (%)

 

30.93

16.14

DF= degree of freedom; STY=Straw yield, HI=Harvest index CV= Coefficient of Variation, ns, *, ** and *** = non-significant, significantly different at 5 %, 1% and 0.1%, respectively

Table 6: The main effects of nitrogen and phosphorous rates on Plant height of rice in 2020.

Nitrogen-rate (kg ha-1)

Plant height(cm)

0

62.57c

46

73.4b

92

77.04b

138

114.9a

LSD(P<0.01)

4.45

Phosphorous rate (kg ha-1)

0

79.9b

23

80.17b

46

85.78a

LSD(P<0.05)

4.75

Mean

89.62

CV (%)

6.37

Means followed by the same letters are not significantly different at 5% level of significant; LSD: Least Significant Difference at 1 and 5% level of significant, CV: coefficient of variation (%).

Table 7: The interaction effect of N and P fertilizer rates on panicle length (cm) of upland rice

 

P2O5 kg ha-1

 

N kg/ha

0

23

46

0

14.5h

16.6g

18.3f

46

19.1ef

19.3def

20.0cde

92

20.1de

19.7de

20.4cd

138

21.9ab

21.1bc

22.6a

LSD(P < 0.05)

 

 

*

CV%

 

 

6.38

ns, *, ** and = non-significant, significantly different at 5 %, and 1% respectively. Means followed by the same letter are not significantly different at 5% level of significance; LSD= least significant difference; CV= coefficient of variance.

Table 8: The interaction effect of N and P fertilizer rates on number effective tiller/m2 of upland rice

 

Phosphorous rate (kg P2O5 ha-1)

Nitrogen rate (kg N ha-1)

0

23

46

0

160.7de

154.7e

215.3c

46

195.8cd

230.9bc

214.4c

92

269.56ab

268.7ab

222.4c

138

196cd

275.3a

225.1c

LSD(P < 0.05)

 

 

46.38*

CV (%)

 

 

18.6

Table 9: Effect of nitrogen fertilizer rate on grain filled per panicle of upland rice.

N rates (N kg ha-1)

Number of filled grain panicle

0

86.42c

46

93.21bc

92

98.13b

138

105.95a

LSD(p < 0.001)

7.64

Mean

95.93

CV (%/)

12.29

Means followed by the same letters are not significantly different at 5% level of significant; LSD: Least Significant Difference at 1 and 5% level of significant, CV: coefficient of variation (%).

Number of

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Citation

Kefale Y, Gebremedhin Z, Tadesse D, Worku T (2026) Response of Rain-Fed Upland Rice (Oryza Sativa L.) to Different Rates of Nitrogen and Phosphorus Nutrients on Vertisols of North Western Amhara, Ethiopia. Ann Environ Sci Ecol 6(1): 9.

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Evaluating Changes in Contaminants of Emerging Concern in Municipal Wastewater Effluents Following Treatment Plant Upgrades

Contaminants of emerging concern (CEC) are known to affect aquatic organisms downstream of wastewater treatment plant effluent discharges. Studies in the Grand River watershed on the small-bodied, benthic rainbow darter (Etheostoma caeruleum) have shown altered gene expression, sex steroid levels, gonad size and expression of intersex (testis-ova) associated with wastewater outfalls. Due to these observed biological impacts, over $450M has been spent by the municipal government to upgrade the two major wastewater treatment plants (WWTP) within the Grand River watershed (Waterloo, Kitchener). In this study we monitored process upgrades at each of the WWTPs between 2010 to 2019 for a suite of chemicals including nutrients, CECs, hormones and total estrogenicity. Effluent samples for select CECs and total estrogenicity were analyzed by LC-MS/MS and yeast estrogen screen (YES) assay, respectively. Estrogenicity of the effluent declined rapidly after upgrades were completed. The removal of key CECs varied depending on their physiochemical properties. Although treatment process upgrades lead to greatly reduced environmental exposure to many CECs such as naproxen, some remain at relatively high concentrations (i. e. carbamazepine) that may continue to represent a risk to the environment.

Nivetha Srikanthan1 , Azar Fattahi1*, E. Katie McCann1 , Leslie M. Bragg1 , Hadi Dhiyebi1 , Diana M. Cardenas-Soraca1 , Pam Law2 , Dominika Celmer-Repin2 , Sonya Kleywegt3 , Wayne J. Parker1 and Mark R. Servos1


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Disastrous Effects of Hurricane Helene in the Southern Appalachian Mountains Including a Review of Mechanisms Producing Extreme Rainfall

Hurricane Helene made landfall near Perry (Latitude 30.1N) in the Big Bend area of Florida with a central pressure of 939hPa. It moved northwards creating devastating damage and loss of life; however, the greatest damage and number of fatalities occurred well to the north around the City of Ashville (Latitude 35.6N) where extreme rainfall fell and some of the strongest wind gusts were reported [1-3]. This paper describes the change in the hurricane’s structure as it tracked northwards, how it gathered tropical moisture from the Atlantic and a turning wind profile between the 850hPa and 500hPa elevations which led to such extreme rainfall. This turning wind profile is shown to be associated with extreme rainfall and loss of life from drowning and landslides around the globe. The area around Ashville suffered 157 fatalities which is a significant proportion of the 250 fatalities so far recorded in the whole United Stares from Helene. This is of extreme concern and should be investigated in detail as the public generally expect the greatest impact from hurricanes to be confined to coastal areas near the landfall site. It is another example of increased death tolls from tropical cyclones moving inland and generating heavy rainfall. As the global population increases and inland centres become more urbanised, run off from such rainfall increases which causes greater devastation.

Jeff Callaghan*


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Elimination of Urinary Fluoride in the Population of Diamaré in Relation to Water Contamination

Introduction: Fluorosis, also known as fluorine poisoning is a disease caused by the disruption of various metabolic pathways, one of which includes calcium metabolism implicated in dental and bone formation due to the replacement of calcium by fluoride ions in bone matrix. The aim of study was to determine the presence of fluorine of the population consuming water contaminated at the Diamaré Division.

Method: A cross sectional analytic study design in 7 villages at the Diamaré division from 1st December 2021 to 30th May 2022 was carried out. Participants who gave consent and filled the selection criteria were included. The socio-demographic characteristics, medical history, eating habits and clinical characteristics of the participants were obtained using a questionnaire. Samples of urine, blood of participants and water were collected for analysis at the Centre for Study and Control of Communicable Diseases at the Faculty of Medicine and Biomedical Sciences of the University of Yaoundé. Fluoride concentration in water and urine. Data entry and analysis was done using Epi info; Associations were derived from bivariate analysis.

Results: We had bore holes, wells and river as water sources used of water for drinking, cooking and household activities. 152 participants were recruited and the most common water source used was bore holes (N=94; 61.84.7%). Some used water from one source only; others from two sources or more. Majority had Joint pains (78.7%). Dental fluorosis accounted for 26%., bowed legs 4.7%, skeletal deformities 6%, immobilization of joints 41.3% and knocked knees 1.3%. A mean water fluoride concentration of 1.30 ±1.68mg/l ranging from 0.04-5.75mg/l was obtained from 30 samples of water collected while that of 2.89 ±2.87mg/l ranging from 0.05-14.35 mg/l was obtained from urine.

Conclusion: The majority of water sources (wells and boreholes) used by our study population for consumption are contaminated with fluoride which is eliminated in urine by the entire population.

Antoine Vayaraï MANAODA1*, SAMIRA Amadou2, YINYANG Jacques1, NGOULE Charles2, ETAME LOE Giselle2 and ADIOGO Dieudonné1


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Commentary Pathways and Therapeutic Targets of Ozone induced Lung Disease

Chronic exposure to ambient Ozone (O3) air pollution induces respiratory inflammation and hyperreactivity, emphysema and interstitial lung fibrosis. O3-induced oxidative stress causes epithelial barrier injury and cell death activating Toll-like receptors, DNA sensing pathways and inflammasomes with production of a range of inflammatory chemokines with a mixed phenotype of COPD and asthma. O3 exposure is often associated with other pollutants causing exacerbation leading to severe respiratory disease. Here, we review mechanisms and therapeutic targets to control O3-induced COPD-like disease.

Remo C. Russo1 and Bernhard Ryffel2,3*


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Heavy Metal Contamination in Seawater in Darsait, Azaibah and Seeb in Oman: An Assessment of Environmental Pollution

This study investigates heavy metal contamination in seawater and sediments in three coastal regions of Oman – Darsait, Azaibah and Seeb. In 2022, sample collections were made in subtidal ecosystems in these three areas, and the samples were analysed to assess the potential environmental impacts of treated wastewater. The study employed a comprehensive sampling strategy adhering to the Oman Environmental Impact Assessment (EIA) Guidelines to evaluate key parameters such as temperature, salinity, dissolved oxygen, and heavy metal concentrations see Appendix 1. Results indicate that the levels of most heavy metals contamination had not changed significantly since the baseline surveys in 2009 and 2012, but that some levels were still above EIA guidelines. Recommendations are made to reduce these levels, ensuring the protection of marine environments and humans while supporting industrial growth. This research contributes to our understanding of anthropogenic impacts on marine ecosystems in Oman and highlights the importance of regular monitoring and adaptive management practices.

Amran Al Kamzari1*, Sulaiman Al Shehhi1, Mohammed Al Kalbani1 and Tim Gray2