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Research Article
Revised

Delta-Aminolevulinic acid dehydratase enzyme activity and susceptibility to lead toxicity in Uganda’s urban children

[version 3; peer review: 1 approved, 1 approved with reservations, 1 not approved]
PUBLISHED 24 Apr 2025
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Abstract

Background

With rapid industrialization, urbanization, and population explosion in sub-Saharan Africa including Uganda, the population has experienced increased exposure to environmental lead subsequently causing extreme (>50μg/dL) and elevated (< 50μg/dL) blood lead levels. For example, means (Blood Lead levels) of 332μg/dL, 120μg/dL, 25μg/dL,11μg/dL, and 10μg/dL in children under 18 years of age in Nigeria, DR Congo, South Africa, Sudan, and Uganda respectively are reported. Susceptibility to lead toxicity correlates with one’s nutrition status, age, and genetics. This study expounded susceptibility to lead toxicity by relating blood lead levels, delta-aminolevulinic acid dehydratase (ALAD) enzyme activity, and genetic variations of proteins that code for ALAD in urban children of Uganda aged between 6 and 60 months.

Methods

A total of 198 blood samples from randomly selected participants, children residing in the Katanga slum of Kampala, Uganda, were analyzed in duplicates for blood lead levels (BLL) on an atomic absorption spectrophotometer, Hemoglobin (Hb) levels, and ALAD enzyme activity were analyzed on a spectrophotometer before DNA extraction, polymerase chain reaction, and restriction fragment length digestion for ALAD polymorphism. The results are presented below.

Results

Geometric means of BLL (10.55μg/dL, SD = 7.4), Hb (7.85g/dL, SD = 1.3) and ALAD enzyme activity (37.15 units/L BLL, S. D = 9.7), corresponded to samples that coded for ALAD1 allele (99.5%) compared to the 0.5% that coded for ALAD2 with BLL (14.5μg/ dL, SD = 4.7), Hb (6.1 g/dL), ALAD enzyme activity (33.8 units/L, SD=1.45). There was a significant relationship with a negative linear correlation between BLL, Hb (status, and ALAD enzyme activity in the three isozymes (ALAD1-1, ALAD1-2, and ALAD2-2) in the strength of ALAD1-1 (r = 0.42, p-value = 0.02) ˂ ALAD1-2 (r = 0.62, effective size = 0.43, p-value = ˂ 0.001) ˂ ALAD2-2 (r = 0.67, effective size = 0.86, p-value = ˂ 0.001).

Keywords

Blood Lead levels, Lead toxicity susceptibility, d-aminolevulinic acid dehydratase enzyme activity, d-aminolevulinic acid dehydratase gene polymorphism.

Revised Amendments from Version 2

  • Updated and added new references.
  • Improved the statistical tables.
  • Improved the discussion section and tailored it to the results of the study.

To read any peer review reports and author responses for this article, follow the "read" links in the Open Peer Review table.

Introduction

Like many other African countries, Uganda is faced with rapid economic development, industrialization, population explosion, and urbanization.1 These transitions are coming with both environmental and health challenges. Population explosion is putting pressure on the environment through increased anthropogenic activities, and elevated volumes of electronic wastes, and this has resulted in increased volumes of toxic pollutants like lead in both air and water bodies.1 Because lead is an accumulative toxin, its increased concentration in the environment continues to cause health challenges, especially for children.25 Lead is an environmental contaminant at high- and low-exposure levels.6,7 However, levels that are deemed low enough to be safe are still detrimental to the developing central nervous system in children as lead is a neurotoxin with no safe level of exposure.710 Elevated environmental lead levels usually correlate with the blood lead levels in exposed individuals.11 Childhood lead exposure is associated with various health challenges that include lung, stomach, and bladder cancers, anemia, neurocognitive disorders, intelligence quotient (IQ) lowering, and stunted growth.5,12 Although environmental lead pollution is preventable, little attention is accorded to this preventable problem in many African countries including Uganda. Recent studies conducted in different parts of Kampala slums report elevated blood lead levels, especially among children.4,13 One’s susceptibility to lead toxicity is modulated by age, genetics, nutrition, and malaria infection status.4,1416 The rate of lead ion absorption, especially in the intestines, is further shown to increase with a decrease in hemoglobin levels. Following its absorption, approximately 98–99% of the lead in the bloodstream is bound to erythrocytes, where it exerts a destabilizing influence on cellular membranes.17

2deltaALAporphobilinogen+2H2O

Within red blood cells, lead reduces cell membrane flexibility and elevates the rate of erythrocyte breakdown, leading to anemia. Lead further specifically binds the delta-aminolevulinic acid dehydratase (ALAD) enzyme which is important in the heme biosynthetic pathway. This enzyme is involved in the condensation of glycine and succinyl CoA, and decarboxylation into delta-aminolevulinic acid (ALA) during the initial step of heme synthesis that takes place in the mitochondria before subsequent intermediate steps that take place in the cytoplasm and mitochondria again.

Porphobilinogen is formed by combining two molecules of δ-ALA with the help of the enzyme δ-aminolevulinic acid dehydratase (δ-ALAD) in the cytosol.

Subsequently, the enzyme ferrochelatase in the mitochondria facilitates the incorporation of a ferrous ion (Fe2+) into protoporphyrin IX to create heme. Delta-ALAD plays a vital role in lead poisoning, as its inhibition reduces heme production, leading to an increase in δ-ALA levels in the blood and urine of individuals exposed to lead. The synthesis of heme is not significantly affected until δ-ALAD activity is inhibited by 80–90%,18 which typically happens at a blood lead concentration of around 55 μg/dL.

The enzyme ALAD is rich with thiol groups and zinc ions, that have a high affinity for lead ions and this renders the enzyme more sensitive to attack by circulating lead ions.19,20 It is a tetramer homodimer with eight identical subunits and is located in the cytoplasm. In each of its subunits, it binds eight zinc atoms, where four zinc molecules act as catalysts, whereas the remainder serves as tertiary structural stabilizers. In times of lead burden, lead ions displace zinc from the enzyme’s active site and inhibit its activity, resulting in the accumulation of ALA.21 Accumulated levels of ALA trigger the production of reactive oxygen species (ROS), which are associated with oxidative stress.

Lead-induced oxidative stress results from the production of reactive oxygen species (ROS) and depletion of antioxidant reserves, particularly glutathione (GSH).22,23 Lead interacts with GSH and antioxidant enzymes, inhibiting their functions and disrupting redox balance. Lead also interferes with essential cations, affecting various biological processes. Its ability to cross the blood-brain barrier and disrupt protein kinases can lead to neurological deficits.24 Lead may induce DNA damage, inhibit repair mechanisms, and alter gene expression even at low concentrations.25 Ingestion of lead ions can impact enzyme activities, protein levels, and blood parameters.14 Preventive antioxidant measures are crucial in mitigating lead-induced oxidative damage, as complete lead removal from the body is challenging.26,27 The oxidative stress induced by lead triggers harmful chain reactions, leading to lipid peroxidation, protein and DNA damage, and potential carcinogenic effects.28 Lead’s impact on cell membranes and signaling processes further exacerbates its toxic effects.

Several studies from different regions indicate varying blood lead levels, biological markers, and even symptoms among people in the same locality. For example, lead toxicity impairs the Vitamin D receptor (VDR), and induces polymorphism at the High Fe (HFE) and ALAD genes. Polymorphism at the HFE gene produces C282Y and H63D mutants while ALAD-1 &2 variants at the ALAD gene. Polymorphism of the ALAD gene is reported to modulate one’s susceptibility to lead toxicity.29,30 The ALAD enzyme is encoded by a single gene on chromosome 9q34 region.31 This gene codes for two alleles i.e., ALAD-1 and ALAD-2,32 which are codominant (Single Nucleotide Polymorphism database (dbSNP) ID: rs1800435 [http://www.ncbi.nlm.nih.gov/SNP/index.html]. Their expression results in a polymorphic enzyme system consisting of three different isozymes: ALAD1-1, ALAD1-2, and ALAD2-2. Individuals dominantly expressing ALAD1-2 and ALAD2-2 have a higher susceptibility to lead toxicity than those expressing the ALAD1-1 isozyme. The prevalence of the ALAD-2 allele is race-specific and usually ranges from 0 to 20 percent.29 Therefore, the ALAD polymorphism affects and modifies lead metabolism and delivery to target organs.33 To date, no study regarding ALAD enzyme activity and polymorphism distribution in the Ugandan population has been conducted. The present study, therefore, aimed at expounding on the ALAD enzyme activity, and the distribution of ALAD genotypes to lead exposure susceptibility in Ugandan children. Thus, this is the first study to address lead exposure susceptibility, ALAD enzyme activity, and polymorphism in Ugandan children.

Methods

Ethical considerations

Gulu University Research Ethics Committee approved study No. (GUREC-048), dated 31/05/2019. The study’s intentions were first clearly explained in English and a local language to the participant’s parents/guardians before they signed informed consent forms.

The study design

This was a cross-sectional study that involved randomly selected children who resided in the Katanga slum of Kampala Uganda (00°18′49″N 32°34′52″E, coordinates) for at least a year. The area has approximately 7000 inhabitants and 15.2% of these are under 5 years of age [http://www.askyourgov.ug]. Children aged between six and sixty months who had resided in the area for at least twelve months were included in the study. Those who had lived in the area for less than twelve months and were above the age of 5 years were excluded from this study.

The sample size (n) for the study was derived from Cochran’s sample size expression;

n=Z2·P·1Pe2

where p; is the population size, e; is the margin of error, and z; is the z-value, extracted from a z-table.

Through their local leaders, the homes of study participants were visited, and explained the purpose of the study was before the signing of consent forms by their parents/guardians. Visibly malnourished children and those with a history of blood transfusion were excluded from this study. Duplicate samples of venous blood (5 ml; n = 198) were drawn from each study participant by qualified nurses and technicians. One tube contained heparin and this was used for hematocrit determination, while the other tube containing ethylenediamine tetraacetic acid (EDTA) was used for other assays. The samples were transported on ice to the Makerere University Biochemistry Department laboratory for analysis.

Assay for blood lead using atomic absorption spectrophotometer

Assay for blood lead using atomic absorption spectrophotometer

Blood lead levels were determined on an atomic absorption spectrophotometer (Agilent MY17180002 200 series) equipped with a graphite tube atomizer (GTA 120), a hollow-cathode lead lamp with a working current of 5 mA, 283.3 nm spectral line, and 0.5 nm bandwidth as described elsewhere.34 Five hundred microliter (500 μl) aliquots of blood samples were mixed with 1.2 ml of a solution that was prepared by mixing equal volumes of 0.5% Triton X-100 and 1% di-ammonium phosphate ((NH4)2HPO4). A total volume of 1.8 ml of deionized water was added to each sample in the tube followed by the addition of 1.5 ml of 20% trichloroacetic acid (TCA) before vortex mixing. The samples were centrifuged at 5000 rpm for 20 min and 10 μl of the supernatant from each was collected and injected into the graphite tube. Lead standard concentrations ranged from 2 μg/dL to 50 μg/dL. Samples were analyzed in duplicate, and their mean values were determined with occasional blanking with deionized/distilled water. The equipment had a detection limit of 2 μg/dL.

Colorimetric determination of hemoglobin levels by blood cyanmethemoglobin reaction method

Hemoglobin levels were determined following a cyanmethemoglobin reaction method described elsewhere.35 Blood samples were processed and analyzed as described in our previous study.11 Briefly, 100 μl of each sample was reacted with cyanide reagent and incubated at room temperature for 15 minutes. Hemoglobin concentration was then determined using a Jenway 6051 colorimeter at 540 nm against a reagent blank.

Determination of hematocrit levels of the study blood samples

The hematocrit levels of the study blood samples were assayed as described elsewhere.36 Whole blood samples in heparinized tubes were forced into narrow-diameter glass capillary tubes to two-thirds levels. The capillary tubes had a self-sealing compound from one end. The capillaries together with the blood were loaded onto a micro hematocrit centrifuge and ran at a relative centrifugal force of 14,000 ×g for five minutes. Following centrifugation, hematocrit levels of each sample were measured within 10 min while the tubes were kept in a horizontal position to avoid merging of the layers. Hematocrit levels were estimated by calculating the ratio of the column of packed erythrocytes to the total length of the sample in the capillary tube.

Determination of delta-aminolevulinic acid dehydratase (ALAD) enzyme activity

The blood δ−ALAD enzyme activity in all the samples collected was measured following a method described by Ref. 37. The ALAD enzyme activity of each sample in duplicate was determined by incubating 0.20 ml of the sample with 1.30 ml of Triton X-100 reagent in disposable plastic tubes and thereafter adding 1 ml of buffered ALA substrate (0.01M). The buffered ALA substrate was prepared by dissolving 0.1676 g of ALA-HCL in 100 ml of phosphate-citrate buffer pH 6.65. The buffer was previously prepared by dissolving 6.703 g/dL Na 2HPO 4 (0.25 M) and citric acid 5.25 g/dL (0.25 M). Aliquots equivalent to 1ml of Trichloroacetic acid (TCA) reagent were added to each sample and the blank (plain distilled water).

1.0 ml of the modified Ehrlich’s reagent was added to both test and blank aliquots. This was previously prepared by dissolving 10 g of p-dimethylaminobenzaldehyde (DMBA) in 420 ml of acetic acid and diluted to 1 L with distilled water. Before storing the reagent at 40°C a working solution was prepared by mixing 50 ml of DMBA-acetic acid with 8 ml of 70% perchloric acid. Following the addition of the modified Ehrlich’s working reagent, the mixtures were allowed to stand for 13 minutes for color development before measurement at 555 nm on a spectrophotometer. The corrected absorbance A = (Test absorbance — the blank absorbance) was used to calculate the enzyme’s activity.

Corrected AbsorbanceA×12500Hematocrit=units of ALAD enzyme activity,

Where 12500 is the blood dilution factor.

Delta-aminolevulinic acid dehydratase (ALAD) genotyping

Blood samples were analyzed for polymorphism as described elsewhere,38,39 Genomic DNA from each blood sample was extracted using a Qiagen genomic DNA purification kit (DNeasy, Catalogue no. 69506) following the manufacturer’s instruction. The resultant DNA products were purified before polymerase chain reaction (PCR) amplification. The PCR reaction mixture equivalent to 50 μL contained 1× buffer (10 mM Tris-HCl, pH 8.8; 50 mM KCl), 2 mM MgCl2, 0.2 mM dNTPs, 20 pmol each primer, and 3U Taq DNA polymerase.

Forward primer, 5′-AGACAGACATTAGCTCAGTA-3′,

and reverse primer, 5′-GGCAAAGACCACGTCCATTC-3′

The running conditions on a Gene Amp PCR system 9700 were; pre-denaturation at 94°C for 5 min, followed by 35 cycles of denaturation at 94°C for 30 s, annealing at 58°C for 30 s, synthesis at 72°C for 1min and final extension at 72°C for 5min. The amplified products (916-bp region of genomic DNA) in volumes of 10 μL were digested overnight with MspI restriction enzyme (2.5 units) in a 20 μL reaction mixture containing 50 mM sodium chloride, 10 mM Tris-HCl, 10 mM magnesium chloride, 1mM dithiothreitol (pH 7.9) at 37°C. The fragments were separated by electrophoresis on a 2% agarose gel stained with ethidium bromide and visualized under a UV illumination system. ALAD1-2 samples had both a 583- and a 512-bp fragment, whereas ALAD1-1 individuals had a single 583-bp fragment.

Data analysis

Results were expressed as means and correlations, and the statistical significance was evaluated by one-way analysis of variance (ANOVA) using Minitab 19 statistical software, an equivalent open-access alternative is Scilab-6.1.1 statistical software. In addition to maximizing data collection, missing data cases were completely omitted (list wise) from the data set before statistical analysis.

Results

Following genotyping of the samples for ALAD alleles, the outcome is shown in Table 1 with corresponding BLL, Hb levels, hematocrit, and ALAD enzyme activities. The results indicate that the ALAD1-1 isozyme was the most predominant with moderately high hemoglobin levels and seemingly normally functioning ALAD enzyme. The frequency of the ALAD2-2 isozyme is shown to be the least predominant (n = 1, BLL = 14.1, ALAD enzyme activity = 33.8, Hb = 6.1, hematocrit volume = 32.9) as compared to the ALAD1-1 and ALAD1-2 isozymes (see Table 1). Comparing the hemoglobin levels across all the groups, it is apparent that members with ALAD2 allele have lower Hb levels compared to members coding for ALAD1.

Table 1. Gene distribution of ALAD (delta-aminolevulinic acid dehydratase) isozymes and the corresponding blood lead levels, ALAD enzyme activity, hemoglobin, and hematocrit volume among the 198 study participants.

Isozyme
Test
ALAD 1-1 ALAD 1-2
Relative Frequency (%) of ALAD isozymes among the study population (N=198)88.9 (176)10.6 (21)
Blood Lead levels (mean) μg/dL8.812.3
ALAD enzyme activity (mean) Units/L39.634.7
Hemoglobin levels (mean) g/dL8.96.8
Hematocrit volume (%) (mean)27.629.2

The results further indicate that members with isozyme ALAD1-1 had their ALAD enzyme activity functioning moderately normal as compared to the rest. Correlational analysis revealed that ALAD enzyme activity and hemoglobin levels strongly correlated with blood lead levels across all the genotypes ( Table 2).

Table 2.

Correlations (Pearson) r and p-values between different ALAD isozymes, blood Lead levels, ALAD enzyme activity, hemoglobin levels and hematocrit volumes.

Isozyme
Test
ALAD 1-1 (n = 176)ALAD 1-2 (n =21) ALAD 2-2 (n =1)
Blood Lead levels μg/dLr = 0.42, p-value 0.02r = 0.66, p-value ˂0.001r = 0.51, p-value ˂0.001
ALAD enzyme activity Units/Lr = 0.62, p-value ˂0.001r = 0.71, p-value ˂0.001r = 0.69, p-value ˂0.001
Hemoglobin levels (g/dL)r = 0.67, p-value ˂0.001r = 0.71, p-value ˂0.001r = 0.64, p-value ˂0.001
Hematocrit volume (%)r = 0.11, p-value ˂0.07r = 0.16, p-value 0.06r = 0.12, p-value 0.11

Discussion

The research explored the relationship between the ALAD enzyme activity and blood lead levels in Ugandan urban children aged 6-60 months. This age group was selected since it’s known to be more susceptible to even what would be safe levels of Lead than adults.7,8,10 The adverse effects of exposure to lead on human health are well known. It has also been reported that elevated environmental lead levels usually correlate with blood lead levels in exposed individuals.11 This study found that most individuals sampled (99.5%) had the ALAD1 gene, while (0.05%) carried the ALAD2 gene, which agrees with previous studies.38,40,41 While ALAD1 individuals are more susceptible to lead toxicity and reduced hematocrit levels, this study’s findings showed the contrary. This could be due the low lead exposure, environmental stimulation of red blood cell production, or other physiological factors. ALAD2 individuals exhibited higher blood lead levels than ALAD1, this could have been due to altered exposure to body dynamics. In times of prolonged lead exposure, and because of higher lead–binding affinity, ALAD2 variants tend to exhibit increased accumulation of lead in the red blood cells hence effectively elevating total blood lead levels.42 Since ALAD2 binds lead more tightly, more lead may remain detectable in blood compared to ALAD1 individuals where lead is rapidly distributed into soft tissue and bones. Additionally, during bone turnover especially in growth spurts in children, lead stored in bones is easily released into the bloodstream.43 In ALAD2 individuals, released lead binds ALAD2 enzymes more readily, hence, the levels of available blood lead may potentially increase compared to counterparts with ALAD1 where less lead binds to the red blood cells. Furthermore, in times of recent or acute exposure, ALAD2 individuals tend to temporarily show elevated lead levels due to efficient lead binding and a slower rate of lead excretion via urine and feces as compared to ALAD1 individuals.44,45 The elevated hematocrit levels in the ALAD2 individual who is anemic, could be associated with elevated stress and hemolysis which could potentially affect hemoglobin production or even damage to the existing red blood cell, leading to the paradoxical scenario of low Hb observed. Elevated hematocrit levels could also increase red cell production particularly if the individual was dehydrated or had had low plasma volume and this potentially concentrates red blood cells.

Conclusion

The study also highlights that the ALAD genotype is significantly linked to Hb levels, ALAD enzyme activity, and blood lead levels, with individuals carrying the ALAD2-2 gene showing higher lead levels compared to those with ALAD1-2 and ALAD1-1 genes. This underscores the significance of ALAD polymorphism in altering how the body processes lead and suggests the need for more extensive research involving a larger population in Uganda to gain a deeper understanding of how ALAD gene variations impact lead toxicity.

Study limitation

For better results on the effect of persistent exposure to low levels of lead, the study participants’ age range should have been from six months to eighteen years.

This study did not look at the nutritional status of the study participants which is important for lead toxicity susceptibility.

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mukisa A, Kasozi D, Aguttu C and Kyambadde J. Delta-Aminolevulinic acid dehydratase enzyme activity and susceptibility to lead toxicity in Uganda’s urban children [version 3; peer review: 1 approved, 1 approved with reservations, 1 not approved]. F1000Research 2025, 11:538 (https://doi.org/10.12688/f1000research.108885.3)
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Version 2
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PUBLISHED 06 Jun 2024
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Reviewer Report 11 Nov 2024
Howard Hu, Department of Population and Public Health Sciences, Keck School of Medicine, University of Southern California, Los Angeles, California, USA 
Not Approved
VIEWS 33
  • The subjects of this report are novel and important, in that lead exposure remains one of the top environmental health problems in the world, whereas studies of lead exposure (with blood lead as a biomarker of exposure)
... Continue reading
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Hu H. Reviewer Report For: Delta-Aminolevulinic acid dehydratase enzyme activity and susceptibility to lead toxicity in Uganda’s urban children [version 3; peer review: 1 approved, 1 approved with reservations, 1 not approved]. F1000Research 2025, 11:538 (https://doi.org/10.5256/f1000research.167147.r335186)
NOTE: it is important to ensure the information in square brackets after the title is included in all citations of this article.
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Reviewer Report 14 Jun 2024
Lorenz S. Neuwirth, SUNY Neuroscience Research Institute, Old Westbury, New York, USA 
Approved
VIEWS 6
Abstract:
In the abstract, the conclusion should contain more information containing a discussion of the results and then the conclusion. As it reads, it is incomplete.

Introduction:
It may just be the formatting of how ... Continue reading
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Neuwirth LS. Reviewer Report For: Delta-Aminolevulinic acid dehydratase enzyme activity and susceptibility to lead toxicity in Uganda’s urban children [version 3; peer review: 1 approved, 1 approved with reservations, 1 not approved]. F1000Research 2025, 11:538 (https://doi.org/10.5256/f1000research.167147.r287537)
NOTE: it is important to ensure the information in square brackets after the title is included in all citations of this article.
Version 1
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PUBLISHED 18 May 2022
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Reviewer Report 09 Aug 2023
Lorenz S. Neuwirth, SUNY Neuroscience Research Institute, Old Westbury, New York, USA 
Approved with Reservations
VIEWS 10
In the abstract the language is unclear in the following:
  1. Background: it should read "in sub-Saharan Africa the population of Uganda has experienced increased  environmental exposures to lead as a contaminant that subsequently has caused elevated
... Continue reading
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Neuwirth LS. Reviewer Report For: Delta-Aminolevulinic acid dehydratase enzyme activity and susceptibility to lead toxicity in Uganda’s urban children [version 3; peer review: 1 approved, 1 approved with reservations, 1 not approved]. F1000Research 2025, 11:538 (https://doi.org/10.5256/f1000research.120325.r184451)
NOTE: it is important to ensure the information in square brackets after the title is included in all citations of this article.
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Reviewer Report 09 Jun 2022
Muhammad Sajid Hamid Akash, Department of Pharmaceutical Chemistry, Faculty of Pharmaceutical Sciences, Government College University, Faisalabad, Pakistan 
Approved with Reservations
VIEWS 18
This manuscript describes in detail the role of ALAD (delta-aminolevulinic acid dehydratase) in enzymatic activity and its susceptibility to lead toxicity in urban children of Uganda. This study seems interesting, but there are certain flaws and shortcomings that need careful ... Continue reading
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Akash MSH. Reviewer Report For: Delta-Aminolevulinic acid dehydratase enzyme activity and susceptibility to lead toxicity in Uganda’s urban children [version 3; peer review: 1 approved, 1 approved with reservations, 1 not approved]. F1000Research 2025, 11:538 (https://doi.org/10.5256/f1000research.120325.r138566)
NOTE: it is important to ensure the information in square brackets after the title is included in all citations of this article.

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Not approved - fundamental flaws in the paper seriously undermine the findings and conclusions
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