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Lead (Pb) and cadmium (Cd) blood levels and potential hematological health risk among inhabitants of the claimed hazardous region around Qaroun Lake in Egypt 

Background: Lead (Pb) and cadmium (Cd) heavy metals are considered potentially hazardous toxins which cause serious health problems. Many studies reported that the water of Qaroun Lake in Fayoum, Egypt with its fish farms was contaminated with Pb and Cd above permissible levels. However, there is a lack of studies addressing levels of these toxic metals among inhabitants. Objectives: We aimed to evaluate blood levels of Pb and Cd and their potential health risk among inhabitants around Qaroun Lake. Materials and methods: This case-control study estimated Pb and Cd blood levels among 190 individuals from two destinations (near and far away) of Qaroun Lack using an atomic absorption spectrometer after full history taking and routine checkup investigations; Full blood count, serum ferritin, liver enzyme (ALT), and creatinine levels. Results: There was a significant difference between blood levels of Pb and Cd heavy metals of inhabitants from near and far away Qaroun Lake destinations (p-value < 0.001). The majority of inhabitants around Qaroun Lake had Pb and Cd blood levels above permissible levels (100% and 60% respectively). Critical levels out of them were 12.1% and 30.3% respectively. In comparison to inhabitants faraway Qaroun Lake, three individuals (2.4%) had Cd above the permissible level, while all of them (100%) had Pb level within the permissible level. There were no statistically significant differences between the two sampled populations as regards hemoglobin level, ALT, creatinine, and ferritin serum levels (p-value > 0.05). The difference between studied populations regarding types of anemia was not statistically significant. Subclinical leucopenia was higher in the population near Qaroun Lake when compare to inhabitants far from the lake (13.6% vs. 4.8%, p-value 0.032). Conclusion: Bio-monitoring of populations exposed to Pb and Cd hazardous substances could help in generating an early warning system to reduce the disease burden associated with their toxicity.

Keywords: Lead; Cadmium; Wadi El-Rayan; Qaroun; Egypt

Introduction

Cadmium (Cd) and Lead (Pb) heavy metals, which are considered potentially hazardous toxins, cause serious health problems. Lead, cadmium, iron, and zinc were reported to be the commonest toxic metals that affect human health ([1]). Once a toxic metal enters the body, it distributes through the blood to soft tissues (e.g., liver, kidney, brain), and bones ([2]). Acute and chronic toxic effects of these heavy elements, as a consequence, affect different body organs causing severe complications such as; gastrointestinal disorders, kidney failure, anemia, vascular damage, birth defects, nervous system disorders, and skin lesions ([3], [4]).

Pb is primarily toxic to the nervous system but can also induce anemia by disturbing the heme synthesis pathway ([5]). Cd which has been categorized as carcinogenic for human beings by the International Agency for Research on Cancer is mainly affecting the kidney and can also cause bone demineralization ([6]).

Pb and Cd heavy metals enter the environment from both industry and natural resources; such as volcanic emissions and weathering of rocks, therefore, they are found in air, soil, and water and can subsequently accumulate in plants and animals ([5]). In addition, both Pb and Cd have been used in different industries. Although Pb has unique properties in industries, Cd has declined in the United States of America since 2001 in response to environmental pollution concerns. Lead has been used in the manufacturing of batteries, painting, plumbing, mining, pipes, and metal recycling, while Cd is used in nonferrous alloys, batteries, plastic stabilizers, pigment production, coatings, and plating ([6]).

According to the Centers for Disease Control and Prevention (CDC), the average concentration of blood Pb among healthy unexposed adults was estimated at 0.9 ug/dL. The estimated reference values of permissible Pb blood levels are < 5ug/dL in adults and < 3.5 ug/dL in children, while the critical/ hazardous levels are ≥ 70 ug/dL in adults and ≥ 20 ug/dL in children ([7], [8]). The average range of Cd blood level of healthy unexposed adults is 0.1–4 µg/L. The estimated reference value of the permissible Cd blood level is ≤ 0.4 ug/L, while the critical value is > 5 ug/dL ([9]).

Generally, the primary source of Pb and Cd exposure is contaminated food. Leafy vegetables in general including Tobacco leaves contain high levels of Cd due to bioaccumulation from the soil ([9], [10], [11]). However, in the United States, nonsmoker individuals who regularly consume shellfish and organ meats will have a higher Cd exposure risk ([9]). Because both Pb and Cd elements have no known biological role in the human body, the Joint Expert Committee on Food Additives (JECFA), an international scientific committee of the Food and Agriculture Organization of the United Nations in collaboration with the World Health Organization has established the safe level of provisional tolerable monthly intake (PTMI) of Cd and Pb heavy elements of 25 µg/kg of body weight ([12]).

Many studies reported that contamination of freshwater with heavy metals with subsequent contamination of aquatic organisms, particularly fish, has become a matter of critical concern ([13], [14]). Previous studies that evaluated the level of heavy metal in Lake Qaroun in El-Fayoum Governorate and its fish farms found that some toxic heavy metals, particularly lead, iron, zinc, and cadmium were higher than the permissible level ([15], [16], [17], [18]). However, there is a lack of studies that evaluated these toxic heavy metals among inhabitants around the tourist Qaroun Lake. Hence, the present study is aiming to evaluate the level of lead and cadmium metals in the blood of inhabitants of the region around Qaroun Lake of Fayoum Governorate in Egypt and to assess their potential health risks.

Materials and methods

Study design and sample population

This case-control study, which was carried out in Fayoum Governorate of Egypt during the period from October to December 2022 from two destinations (near and far away) of Qaroun Lack as per the Declaration of Helsinki ethical standards and after taking the approval of the ethical committee of Faculty of Medicine Fayoum University (Fig. 1). The sample size was calculated using (G power version 3.1.9.4) to get a power level of 0.90, an alpha level of 0.05, and a medium effect size of 0.5 for Pb and Cd blood levels between the two study areas. We assumed 1:2 as a ratio between the two destinations, so the sample size was estimated to be 64 and 128 in the areas near and far away from Qaroun Lake, respectively. The final study sample was 190 participants including 66 and 124 inhabitants from areas near and far away from Qaroun Lake, respectively.

Graph: Fig. 1Ibshwai and Tamia Districts located around Qaroun Lake in Fayoum Governorate in Egypt

Full history taking and clinical examination that addressed the risk of exposure to Pb and Cd either environmental or occupational risk, as well as, any expected medical outcomes manifestation. Peripheral venous blood samples withdrew from each participant with informed consent into serum and ethylene diamine tetra acetic acid (EDTA) Becton Dickinson vacutainer tubes (BD, Franklin Lakes, NJ, USA). Routine checkup investigations including Full blood count (CBC), serum ferritin, ALT liver enzyme, and serum creatinine levels were performed for the study population. Pb and Cd heavy metals were analyzed in serum samples of the participants using an atomic absorption spectrometer after sample separation and digestion using the ISO standard methods for determination of Pb and Cd levels.

Metal analysis in blood samples

Sample digestion

The sample digestion occurred depending on the ISO standard methods for wet digestion samples DIN EN 13805 ([19]). A weight in the range of 0.25 g of the sample was placed in the digestion vessel (DAP 60), then 1.25 ml of concentrated nitric acid (Merck, Germany) was added to it. After fumes volatilization under the fume hood, the digestion vessels are sealed and placed in the microwave (Berghof, Germany). The digestion program starts by raising the temperature to 160°C at a rate of 5°C / minute, then increasing to 190°C at a rate of 1°C/minute. At the end of the digestion cycle, the temperature is reduced to 75°C at the rate of 1°C/minute.

Determination of lead and cadmium concentration

Agilent atomic absorption spectrometer equipped by graphite furnace unit model 240ZAA (Agilent Technologies, Germany) was used to determine cadmium (Cd) and lead (Pb) concentrations according to EN 14084:2003 ([20]). The temperature program used for these elements is as fellow:

step

Cadmium (Cd)

Lead (Pb)

Temp. (°C)

Time (sec)

Flow (L/min)

Temp. (°C)

Time (sec)

Flow (L/min)

1

85

5

0.3

85

5

0.3

2

95

40

0.3

95

40

0.3

3

120

10

0.3

120

10

0.3

4

250

5

0.3

400

5

0.3

5

250

1

0.3

400

1

0.3

6

250

2

0

4000

2

0

7

1800

0.8

0

2100

0.9

0

8

1800

2

0

2100

2

0

9

1800

2

0.3

2100

2

0.3

The used method was validated using the average percent recovery and standard deviation plotted into a quality control chart. The quality control sample was carried out with every set of samples by spiking the sample with known concentrations of lead and cadmium. The data of the quality control samples was used to calculate recovery percent, which was determined as an average of 95% and to ensure the accuracy and the precision of the method used.

Statistical data analysis

Statistical Package for Social Sciences (SPSS 22) was used for data statistical analysis. For lead and cadmium levels, median and interquartile range (IQR) were estimated. In comparing the two studied inhabitants, the Mann-Whitney U test was used. Categorical data were presented as frequencies and percentages. For comparing categorical data, the χ2 test or Fischer exact test was performed. P values less than 0.05 was considered to be statistically significant.

Results

The present study enrolled 190 residents aged (3–80 years) from two different districts located around Qaroun Lake in Fayoum Governorate in Egypt, where Ibshwai province located nearby the lake and Tamia province located far away from the lake were selected (Fig. 1). Only (10%) of the total population practiced risky occupations relevant to Pb and Cd heavy metal toxicity. There were no significant differences between the two studied populations as regards age, sex, house, and occupation. There were statistically significant differences between the two studied groups as regards working in farming, smoking, and consumption of fish being higher in inhabitants of regions far from Qaroun Lake (p-value: 0.037, 0.001, 0.029 respectively) (Table 1). The prevalence of abortion and birth defects was higher in areas far from the lake as compared to those near the lake. The sociodemographic and clinical characteristics of the two groups of the study population are presented in Table (1).

Table 1 Sociodemographic and Clinical Characteristics among Sample Population:

Variables

Population Near Qaroun Lake

(n = 66)

Population Distant Qaroun Lake

(n = 124)

P-value

No. (%)

No. (%)

Age (years)

3–17

15 (22.7%)

23 (18.5%)

0.546

18–39

27 (40.9%)

50 (40.3%)

40–59

23 (34.8%)

44 (35.5%)

60–80

1 (1.5%)

7 (5.6%)

Sex

Male

21 (31.8%)

46 (37.1%)

0.468

Female

45 (68.2%)

78 (62.9%)

Occupation

Not working

56 (84.8%)

85 (68.5%)

0.051

Risky**

4 (6.1%)

15 (12.1%)

Not risky

6 (9.1%)

24 (19.4%)

Previous working in farming

Yes

1 (1.5%)

13 (10.5%)

0.037*

No

65 (98.5%)

111 (89.5%)

Previous work in painting

yes

0 (0%)

1 (0.8%)

1.000

No

66 (100%)

123 (99.2%)

Smoking

Smoker

0 (0%)

18 (14.5%)

0.001*

Non-smoker

65 (98.5%)

98 (79.0%)

Ex-smoker

1 (1.5%)

8 (6.5%)

House

Old

33 (50%)

72 (58.1%)

0.287

New

33 (50%)

52 (41.9%)

Eating fish

Once/ week

5 (7.6%)

11 (8.9%)

0.029*

3 times/ month

7 (10.6%)

25 (20.2%)

2 times /month

33 (50%)

70 (56.5%)

Never

21 (31.8%)

18 (14.5%)

Abortion

Yes

6 (13.3%)

25 (32.1%)

0.021*

No

39 (86.7%)

53 (67.9%)

Birth defects

Yes

2 (4.4%)

23 (29.5%)

0.001*

No

43 (95.6%)

55 (70.5%)

Chronic diseases

Diseased

8 (12.1%)

19 (15.3%)

0.547

Non-diseased

58 (87.9%)

105 (84.7%)

HTN

Hypertensive

1 (1.5%)

14 (11.3%)

0.017*

Non-hypertensive

65 (98.5%)

110 (88.7%)

DM

Diabetic

1 (1.5%)

7 (5.6%)

0.177

Non-diabetic

65 (98.5%)

117 (94.4%)

*Significant at p < 0.050, ** Occupations related to exposure to heavy metals, ***IDA: Iron deficiency anemia

Although more than one-third of the study population (74/190, 38.9%) was anemic, only less than one-fifth of them (14.3%) had chronic diseases with no statistically significant differences between the two studied populations (p-value 0.594 and 0.547 respectively) (Table 1).

Regarding hematological lab findings, out of a total of 66 inhabitants with microcytic hypochromic anemia, only 24 (12.63%) were iron deficiency anemia (IDA) confirmed with serum ferritin levels below normal cutoff value for gender and age. Additionally, subclinical leucopenia was higher in the population near Qaroun Lake when compare to those far from the lake (13.6% vs. 4.8% with a p-value of 0.032) (Table 2). Regarding liver and renal function tests, there were no statistically significant differences between the two sampled populations as regards ALT, creatinine, and ferritin (p-value > 0.05) (Table 2).

Table 2 Comparison between Hematological and Routine Laboratory Checkup Parameters of Sample Population:

Laboratory Investigations

Population Around Qaroun Lake

(n = 66)

Population Distant

Qaroun Lake

(n = 124)

P- value

No. (%)

No. (%)

White Blood Cell Count

- Normal count (4–11 109/L)

- Leucopenia

57 (86.4%)

118 (95.2%)

0.032****

9 (13.6%)

6 (4.8%)

Hemoglobin Conc.

- Normal conc. (11.5–17.5 g/dL)

- Anemic level

42 (63.6%)

74 (59.7%)

0.594

24 (36.4%)

50 (40.3%)

Subclinical MHA*:

- Anemic

- Non-anemic

23 (34.8%)

43 (34.7%)

0.981

43 (65.2%)

81 (65.3%)

Subclinical IDA**

- Iron deficiency

- Non-iron deficiency

5 (21.7%)

19 (44.2%)

0.071

18 (78.3%)

24 (55.8%)

Mentzer screening index (< 14) ***

- Positive

- Negative

1 (4.4%)

7 (16.3%)

0.179

22 (95.6%)

36 (83.7%)

MHA with uncertain etiology#

17 (73.9%)

17 (39.5%)

0.039****

Serum Ferritin

- Normal range (Male: up to 300 – Female: up to 200 ug/L)

- Low level

- High level

49 (74.2%)

90 (72.6%)

0.970

16 (24.2%)

32 (25.8%)

1 (1.5%)

2 (1.6%)

ALT

- Normal range (Up to 40 IU/L)

- High serum level

62 (93.9%)

118 (95.2%)

0.719

4 (6.1%)

6 (4.8%)

Serum Creatinine

- Normal range (Male: 1.1–1.4 mg/dl; Female: 0.6–1.1 mg/dl)

- High serum level

65 (98.5%)

116 (93.5%)

0.127

1 (1.5%)

8 (6.5%)

*MHA: Microcytic Hypochromic Anemia among the anemic study population. **IDA: Iron deficiency anemia. ***Mentzer index (MCV/ RBCs) calculated among individuals with microcytic hypochromic anemia < 14 suggestive of thalassemia trait. ****Significant at p < 0.050. # MHA after exclusion of those cases due to IDA and positive Mentzer with suspicious thalassemia trait

There was a significant difference between blood levels of Pb and Cd elements of inhabitants from near and far away Quaron Lake destinations (p-value < 0.001). The majority of inhabitants around Qaroun Lake had Pb and Cd blood levels much above permissible levels established by the CDC (100% and 60.6% respectively). Critical levels out of them were 12.1% and 30.3% respectively. In comparison to inhabitants faraway Qaroun Lake, three individuals (2.4%) had Cd above the permissible level, while all of them (100%) had Pb level within the permissible level (Table 3). The median (IQR) blood concentration for Pb and Cd among our study population near Qaroun Lake was 36.25 (26.20–48.78) ug/dL and 1.45 (0–7.90) ug/dL, respectively. Whereas, their median (IQR) values among those who live far away from the lake were 0 (0–1.7) ug/L and 0 (0–0) ug/L, respectively (Fig. 2).

Table 3 Prevalence of Pb and Cd in Blood of Sample Population

Blood/ Serum Level

Population Around Qaroun Lake

(n = 66)

Population Distant Qaroun Lake

(n = 124)

P- value

No. (%)

No. (%)

Lead

(Pb)

Permissible blood level

(Children < 3.5 ug/dl; Adult < 5 ug/dl)

0 (0%)

124 (100%)

< 0.001*

Above permissible level

58 (87.9%)

0 (0%)

Critical/ Hazardous level

(Children ≥ 20 ug/dl; Adult ≥ 70 ug/dl)

8 (12.1%)

0 (0%)

Cadmium (Cd)

Permissible blood level (≤ 0.4 ug/L)

26 (39.4%)

121 (97.6%)

< 0.001*

Above permissible level

20 (30.3%)

3 (2.4%)

Critical/ Hazardous level (≥ 5 ug/L)

20 (30.3%)

0 (0%)

*Significant at p < 0.050

Graph: Fig. 2Jitter plot with median (IQR) for blood Pb and Cd levels in both study population

In inhabitants around Qaroun Lake, our results found that the critical Pb levels were detected more among younger age groups rather than other age categories (p-value 0.036) (Table 4), however, there were no statistically significant differences between the studied heavy metals (Pb and Cd) blood levels and occurrence of noteworthy clinical/ subclinical manifestations (p-value > 0.05) (Table 5). Though the most obvious clinical/ subclinical manifestation among them was microcytic hypochromic anemia, the majority (17 out of 66 individuals, 73.91%) of them were diagnosed without a clear conclusive underlying etiology (Table 2). Out of a total of 23 inhabitants with microcytic anemia, only 5 (21.7%) had iron deficiency and another had suspicious thalassemia traits by using the Mentzer screening index [[21]].

Table 4 Association between Impermissible Blood Levels of Pb and Cd and Basic Characteristics of Inhabitant near Qaroun Lake in Fayoum Governorate:

Variables

Lead (Pb)

(n = 66)

Cadmium (Cd)

(n = 66)

Critical

(n = 8)

Under-critical/ Impermissible (n = 58)

Critical/ Impermissible

(n = 40)

Permissible

(n = 26)

No. (%)

No. (%)

No. (%)

No. (%)

Age (years)

3–17

5 (62.5%)

10 (17.2%)

10 (25.0%)

5 (19.2%)

18–39

1 (12.5%)

26 (44.8%)

15 (37.5%)

12 (46.2%)

40–59

2 (25.0%)

21 (36.2%)

15 (37.5%)

8 (30.8%)

60–80

0 (0.0%)

1 (1.7%)

0 (0.0%)

1 (3.8%)

P-value

0.036*

0.520

Sex

Male

4 (50.0%)

17 (29.3%)

13 (32.5%)

8 (30.8%)

Female

4 (50.0%)

41 (70.7%)

27 (67.5%)

18 (69.2%)

P-value

0.253

0.883

Occupation

Not working

8 (100%)

48 (82.8%

33 (82.5%)

23 (88.5%)

Risky occupation

0 (0.0%)

4 (6.9%)

3 (7.5%)

1 (3.8%)

Non-Risky occupation

0 (0.0%)

6 (10.3%)

4 (10.0%)

2 (7.7%)

P-value

0.444

0.777

House

Old

3 (37.5%)

30 (51.7%)

21 (52.5%)

12 (46.2%)

New

5 (62.5%)

28 (48.3%)

19 (47.5%)

14 (53.8%)

P-value

0.708

0.614

Eating fish

One/week

0 (0.0%)

5 (8.6%)

1 (2.5%)

4 (15.4%)

Three/month

1 (12.5%)

6 (10.3%)

2 (5.0%)

5 (19.2%)

Two/month

5 (62.5%)

28 (48.3%)

24 (60.0%)

9 (34.6%)

Never

2 (25.0%)

19 (32.8%)

13 (32.5%)

8 (30.8%)

P-value

0.768

0.037*

Abortion

Yes

0 (0.0%)

6 (15.0%)

4 (15.4%)

2 (11.1%)

No

4 (100.0%)

34 (85.0%)

22 (84.6%)

16 (88.9%)

P-value

1.000

1.000

Birth defects

yes

0 (0.0%)

2 (5.0%)

1 (3.8%)

1 (5.6%)

No

4 (100.0%)

38 (95.0%)

25 (96.2%)

17 (94.4%)

P-value

1.000

1.000

*Significant at p < 0.050

Table 5 Association between Pb and Cd Blood Levels and Clinical/ Subclinical Manifestation of Inhabitants near Qaroun Lake in Fayoum Governorate:

Clinical/ Subclinical Manifestation

Lead (Pb)

(n = 66)

Cadmium (Cd)

(n = 66)

Critical

(n = 8)

Under-critical/ Impermissible* (n = 58)

Critical/ Impermissible

(n = 40)

Permissible

(n = 26)

No. (%)

No. (%)

No. (%)

No. (%)

History of any Chronic diseases

Yes

1 (12.5%)

7 (12.1%)

3 (7.5%)

5 (19.2%)

No

7 (87.5%)

51 (87.9%)

37 (92.5%)

21 (80.8%)

P-value

1.000

0.247

History of HTN

Yes

0 (0.0%)

1 (1.7%)

1 (2.5%)

0 (0.0%)

No

8 (100.0%)

57 (98.3%)

39 (97.5%)

26 (100.0%)

P-value

1.000

1.000

History of DM

Yes

0 (0.0%)

1 (1.7%)

1 (2.5%)

0 (0.0%)

No

8 (100.0%)

57 (98.3%)

39 (97.5%)

26 (100.0%)

P-value

1.000

1.000

Microcytic Hypochromic Anemia

Present

3 (37.5%)

20 (36.2%)

12 (30.0%)

11 (42.3%)

Absent

5 (62.5%)

38 (63.8%)

28 (70.0%)

15 (57.7%)

P-value

1.000

0.305

Subclinical IDA

Present

1 (33.3%)

4 (20.0%)

1 (8.3%)

4 (36.4%)

Absent

2 (66.7%)

16 (80.0%)

11 (91.7%)

7 (63.6%)

P-value

0.539

0.155

Subclinical Leucopenia

Present

0 (0.0%)

9 (15.5%)

7 (17.5%)

2 (7.7%)

Absent

8 (100.0%)

49 (84.5%)

33 (82.5%)

24 (92.3%)

P-value

0.586

0.465

ALT Liver Enzyme

High

0 (0.0%)

4 (6.9%)

3 (7.5%)

1 (3.8%)

Normal

8 (100.0%)

54 (93.1%)

37 (92.5%)

25 (96.2%)

P-value

1.000

1.000

Serum Creatinine

High

0 (0.0%)

1 (1.7%)

0 (0.0%)

1 (3.8%)

Normal

8 (100.0%)

57 (98.3%)

40 (100.0%)

25 (96.2%)

P-value

1.000

0.394

Serum Ferritin

Normal

4 (50.0%)

45 (77.6%)

30 (75.0%)

19 (38.8%)

Low

4 (50.0%)

12 (20.7%)

9 (22.5%)

7 (26.9%)

High

0 (0.0%)

1 (1.7%)

1 (2.5%)

0 (0.0%)

P-value

0.187

0.675

*None of the inhabitants had lead levels within the permissible level

Regarding those inhabitants having microcytic hypochromic anemia with uncertain etiology, there was a statistically significant difference between them being higher among those living near Qaroun Lake with a p-value of 0.039 (Table 2). Out of those 17 individuals with microcytic hypochromic anemia with inconclusive etiology lived near the lake, 17 (100%) had Pb and 5 (29.41%) had Cd above the permissible level.

Discussion

There is no data in the literature on the potential health risks of Pb and Cd heavy metals in the Egyptian population particularly in the region claimed to be potentially polluted, around Qaroun Lake in Egypt. Nevertheless, the previously published studies on the pollution of Lake Qaroun with heavy metals particularly Pb and Cd have been noted [[15]–[18], [22]]. Hence, in this study, we aimed to evaluate the most hazardous of these claimed elements (Pb and Cd) in the blood of 190 inhabitants in Fayoum Governorate from different regions using an atomic absorption spectrometer after sample digestion. This study will be considered a preliminary study to assess the commonest hazardous heavy metals of Lack Qaroun of Fayoum Governorates in Egypt.

The historically renowned Qaroun Lake, a close ecosystem in nature, is located in the north of Fayoum Governorate in Egypt (Fig. 1), where contaminants from El-Bats and El-Wadi drains discharge along with agriculture drainage water of Fayoum province [[17]]. It was reported that such anthropogenic inputs and/ or geological sources contribute to the biodiversity of the water lake, where its original freshwater turned into the currently brackish one. Additionally, the evaporation of water due to the hot climate of the region augments the intensification of heavy metals, salts, and pesticide concentrations in the lake [[15]]. Accordingly, such heavy metals contaminations in Qaroun Lake may have devastating effects on the ecological balance of the aquatic environment, hence on the environmental media such as dust, air, soil, and others [[14], [23]].

Our study results coincide with previous studies in which Pb and Cd concentrations in water samples collected from Wadi EL-Rayan Lakes were higher than the maximum permissible level recommended by Egyptian Environmental law, (48) decision 1992/2013, in the spring/ hot season, but within permissible levels in cold one [[15], [22]]. Furthermore, in correlation, they found that urea and creatinine serum levels in Tilapia fish showed a significant increase. On the other hand, George and his colleagues (2013) reported that Cd concentration in the water samples collected from Wadi El-Rayan Lakes was within the recommended permissible limits (100 µg/L) of the National Environmental Law [[24]], where it ranged from (12 to 16.8 µg/L) in the cold season and from (15.7 to 30.7 µg/L) in the hot one [[16]].

In our study, the median (IQR) blood concentration for Pb among our study population lived near Qaroun Lake was 36.25 (26.20–48.78) ug/dL, while it was 0 (0–1.7) ug/dL among those who lived far away the lake. Although various studies disclosed that the normal value for blood Pb concentration was 42.6 µg/L, different values were also reported for other countries. The mean Pb level in an Amazonian district was 32.77 µg/L, while it was 14.5 µg/L in Australia, 21.3 µg/L in Canada, 12.3 µg/L in the Americas, 65.4 µg/L in Brazil, 33.4 µg/L in Italy, and 19.1 µg/L in Korea [[11]]. In conclusion, our results showed in agreement with previous studies that the level of blood Pb concentration might be influenced by numerous epidemiological and environmental variables such as diet, age, and gender [[25]]. Regarding the median (IQR) of Cd blood level, the value was 1.45 (0–7.90) µg/L among those who lived nearby the lake, but an undetectable level was noted among those who lived far away from the claimed destination of the Qaroun Lake region.

Furthermore, our results found that there were no significant differences between the population who lived nearby Qaroun Lake compared to those who lived far away the lack as regards age, gender, house, and occupation. However, we found that there was a significant difference between blood levels of Pb and Cd heavy elements of inhabitants from the two destinations around Quaron Lake (p-value < 0.001). Inconsistent with previous studies described from Bangladesh ([26]), Mexico ([27]), and Russia ([28]), our results showed that the majority of inhabitants nearby Quaron Lake who had Pb and Cd blood levels much above permissible levels established by the CDC were among the younger age group (p-value 0.036). Although the developing biological systems of the human body particularly the nervous system in children is most sensitive to the effects of Pb blood level ([9]), previous studies similarly revealed that the mean blood lead level was higher in children aged from 6 to 11 years than other age categories ([29]). There is no acknowledged safe blood Pb concentration in children, where cognitive, behavioral, and learning difficulties were reported with low blood Pb concentration even as low as 5ug/dL, the CDC (2021) updated the blood lead reference value in children to 3.5 µg/dL instead of 5 µg/dL for avoiding the serious consequence of lead exposure on children's health ([7]).

On the contrary, Queiroz and his colleagues (2019) reported that blood Pb levels show trends with age and gender being higher in adults and the elderly ([11], [30]–[32]). This point out that the duration of exposure to lead in a residential area is consistently found to be a strong predictor of high blood Pb level ([33]–[35]). Regarding gender variant in this study, though the mean blood Pb and Cd critical levels were not statistically different between males and females, the prevalence was almost the same regarding the critical level of blood Pb level being equal (50%) in both gender but and the prevalence of elevated blood Cd level in females was higher than males. This might be explained by the higher number of females who participated in this study in comparison to males. Controversial results were noted in previous studies conducted in Egypt ([29], [36]), Bangladesh ([37]), Thailand ([38]), and Pakistan ([33]), where the incidence of elevated blood lead concentration was higher in males than females. This might be explained by the different traditional roles of male and female in these societies, where increased outdoor activities and occupational risk for males appears to be involved in this sex-related difference ([29]).

Independent of the level of lead heavy metal intoxication in human body fluids, it was reported that the appearance of clinical manifestations varies from one individual to another depending on the surrounding environmental differences [[31]]. Though the most obvious clinical/ subclinical manifestation among inhabitants living near Qaroun Lake was microcytic hypochromic anemia, the majority (73.91%) of them were diagnosed without a clear conclusive underlying etiology. Regarding those inhabitants having microcytic hypochromic anemia with uncertain etiology, there was a statistically significant difference between them being higher among those living near Qaroun Lake with a p-value of 0.039. Out of those 17 individuals with microcytic hypochromic anemia with inconclusive etiology lived near the lake, had 17 (100%) Pb and 5 (29.41%) Cd above the permissible levels. Additionally, subclinical leucopenia was noted higher in inhabitants of the region nearby Qaroun Lake compared to those far away from the lake (13.6% vs. 4.8% with a p-value of 0.032). Similarly, several published studies have noted that cumulative Pb poisoning is associated with increased potential health risks for hematological disorders particularly anemia [[36], [39]]. However, others reported a non-significant association between the presence of anemia and elevated blood Pb level [[36], [41]].

Though there is no safe level of Pb blood level, previous studies have shown that lead-induced anemia microcytic hypochromic can be easily diagnosed at Pb blood levels higher than 50 µg/dL in adults [[42]]. It was reported that anemia-associated chronic exposure to Pb is the result of both interfering with heme biosynthesis and shortening of red blood cell lifespan [[43]]. The critical effect of Pb in the human body is mainly attributed to cellular enzymatic disruption of δ-aminolevulinic acid dehydratase (ALAD) that is essential in heme biosynthesis with a consequent decrease in various red blood cell hematological parameters (RDW-CV, MCV, MCH, and hematocrit) and potential risk of anemia [[9], [44]].

For the well-known Pb and Cd biogeochemical cycle, these heavy metals are usually absorbed from regional background levels and might be present in drinking water, household dust, and food in which environmental media such as dust, air, soil, and others may have an excess of these toxic heavy elements. According to a study carried out in the region around Qaroun Lake in Fayoum Governorate a region with a characteristic ecosystem, geology, and residency might contribute to overt circulating Pb and Cd levels in the region [[11]]. This might explain the statistically significant differences between the two studied groups as regards working in farming, consumption of fish, smoking, and hypertension despite being higher in inhabitants of the region far from Qaroun Lake.

Though there were no statistically significant difference significant differences between the studied heavy metals (Pb and Cd) blood levels and occurrence of noteworthy clinical/ subclinical manifestations in both kidney and liver functions when ALT, creatinine, and ferritin serum levels have been estimated in all the study population (p-value > 0.05). The present study results, in agreement with previous studies, are considered an alarm to the toxic effect of environmental changes in Qaroun Lack ecosystem for being the final reservoir for most of such heavy metals, where it receives heavy loads of organic and inorganic pollutants via several agricultural drains and huge amounts of raw sewage, agricultural and industrial wastewater discharged into the lake [[46]].

Bio-monitoring of populations exposed to Pb and Cd hazardous substances could help in generating an early warning system to reduce the disease burden associated with their toxicity. However, a mass screening program for both inhabitants and environmental media of the regions nearby Qaroun Lake and Wadi El-Rayan in Fayoum Governorate is mandatory to validate such heavy metals' hazardous impact.

Conclusion

This study could be a preliminary study for bio-monitoring of the Fayoum population who are exposed to the hazardous effect of heavy metals in Lake Qarun water and its farm fish. Hence, to generate an early warning system to reduce the disease burden associated with their increased level and lethal toxicity; such as Alzheimer, kidney failure, and anemia for unknown causes, that are otherwise easily preventable.

Acknowledgements

We thank Ahmed Nabil Mohamed, Demonstrator in the Department of Geography and Geographic Information Systems, Faculty of Art, Fayoum University for his help to elucidate the location of the two selected districts around Qaroun Lake on the map displayed in Fig. (1).

Authors' contributions

S.B: The concept of the study development, clinical laboratory work, and corresponding author to the journal. M.S and E.M: contibuted to laboratory work of heavy metal estimation. E.E, and K.S contributed scientifically to data and sample collection. M.M: Data analysis. All authors contributed in design study questionnaire, writing the original draft of the manuscript, critical revision of the manuscript, and approved its final version.

Funding

Not applicable.

Open access funding provided by The Science, Technology & Innovation Funding Authority (STDF) in cooperation with The Egyptian Knowledge Bank (EKB).

Data Availability

All relevant data are within the paper.

Declarations

Ethical approval and consent to participate

The study was approved by the ethical committee of the Faculty of Medicine, Fayoum University. Written informed consent was obtained from the participants. All study procedures were following the ethical standards of the institutional/ and or national research committee and with the 1964 Declaration of Helsinki.

Consent for publication

Not applicable.

Competing interests

All authors declare there is no conflict of interest.

Publisher's Note

Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.

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By Salwa Bakr; Makram Ahmed Sayed; Karem Mohamed Salem; Enas Mohamed Morsi; Mohamed Masoud and Eman Mahmoud Ezzat

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Titel:
Effect of glycerol concentration on levels of toxicants emissions from water-pipe tobacco smoking (WTS)
Autor/in / Beteiligte Person: Almomen, Salwa ; Aldossari, Mobarak ; Khaleel, Yousef ; Altamimi, Mishal ; Alharbi, Ohoud ; Alsuwaydani, Abdulelah ; Almutairi, Malak ; Alyousef, Sarah ; Hafiz, Radwan ; Alshomer, Faris ; Alqahtani, Amani S.
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Zeitschrift: BMC Public Health, Jg. 23 (2023), Heft 1, S. 1-10
Veröffentlichung: BMC, 2023
Medientyp: academicJournal
ISSN: 1471-2458 (print)
DOI: 10.1186/s12889-023-16740-2
Schlagwort:
  • Waterpipe smoking
  • Waterpipe tobacco
  • Tobacco regulation
  • Public aspects of medicine
  • RA1-1270
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  • Sprachen: English
  • Collection: LCC:Public aspects of medicine
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  • File Description: electronic resource
  • Language: English

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