iodine in drinking water from east african groundwater sources · 2020. 5. 11. · figure 3...

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Expert | Impartial | Innovative Emma Crewdson email: [email protected] Iodine in drinking water from East African groundwater sources E Crewdson 1 , P L Smedley 1 , and A M MacDonald 2 1 British Geological Survey, Keyworth, Nottingham, UK 2 British Geological Survey, Edinburgh, UK The content of iodine in the diet has implications for human health. Chronic deficiency has long been associated with development of iodine-deficiency disorders (IDDs) including goitre. Drinking water, including groundwater, contributes to the dietary iodine intake so establishing the content and distribution in water improves the understanding of dietary sources. However, whilst the prevalence of IDDs is widely reported, iodine is rarely analysed during traditional groundwater health studies. There are also no regulations for either the minimum or maximum concentrations of iodine in drinking water. This study aims to review the distribution of iodine in groundwater-sourced drinking water supplies in areas of Ethiopia, Uganda, Tanzania and Malawi (sample sites shown in Figure 2, summary statistics in Table 1 and 2). The study aims to deduce the sources and mechanisms controlling iodine concentrations in each region. An assessment of the relationships between iodine and other dissolved ions was conducted in order to deduce the processes contributing to iodine content. Preliminary results indicate that the concentration of iodine is related to other dissolved ions. Sulphate, uranium, strontium, sodium and fluoride show the strongest relationships with iodine ( Figure 4), and are in line with the association between iodine and TDS. Iodine content is not simply controlled by the composition of rain water; increases occur in catchments through interactions with rocks and soils. The controls on iodine concentration in drinking water supplies have implications for the dietary intake of iodine and can be particularly marked in isolated populations, where low iodine in groundwater is reflected in crops and livestock of the local area. Work is ongoing to investigate the relationships between iodine and other solutes in the groundwater, and to build a database of groundwater in East Africa. The natural iodine concentrations of the groundwaters will be combined with additional rainfall and aquifer composition data. The results will provide information on the iodine intake of populations with groundwater-sourced drinking water. By characterising the environmental sources and processes behind the iodine content, the results will contribute to wider public health initiatives in the mitigation of iodine deficiency disorders. Figure 3 Boxplots show the distribution of iodine occurring in natural waters in two regions of Ethiopia. * HDW with iodine concentration of 322 μg l -1 excluded from plot, ** HDW with iodine concentration of 62.8 μg l -1 excluded from plot. Figure 4 Relationships are shown between iodine and other elements, grouped by bedrock type. WHO (2011) guideline values indicated, showing maximum recommended concentrations. There are no health-based guideline values for sodium, magnesium, calcium, chloride, sulphate, carbonate or strontium. All samples are below the WHO (2011) guideline value for arsenic (10 μg l -1 ) and uranium (30 μg l -1 ). References Bell, R. (2019). Impact of the 2015/16 El Niño on rural water security in Ethiopia. World Health Organisation (2011). Guidelines for drinking-water quality, fourth edition. Groundwater sources including, springs, shallow boreholes and hand dug wells have been sampled by the British Geological Survey across East Africa (examples of sampled drinking water sources shown in Figure 1). The hydrochemistry data have been compiled into a database for iodine in groundwater from East Africa. Variation in detection limits from the ICP-MS analysis method were accounted for. The preliminary results presented here are based on the iodine content of water from 196 shallow boreholes (BH), 38 hand dug wells (HDW), 18 springs (SP) and 10 rainfall samples. Figure 1 Examples of a shallow borehole (top left), hand dug well (top right) and spring drinking water source (bottom left) in Ethiopia (Bell, 2019). The iodine content of groundwater varies both between source type (Table 1) and regionally (Table 2). Iodine concentrations are lowest in rainfall and springs, and greatest in boreholes and hand dug wells in two regions where data are available (also demonstrated in Figure 3). Water Source Count Min Median Mean Max Water Source Count Min Median Mean Max Boreholes 196 0.3 9.65 37.2 718 Springs 18 2.8 5.56 9.66 44 Hand dug wells 38 2.08 19.5 53.4 322 Rainfall 10 1.8 3.4 4.02 7 Table 1 Summary statistics for iodine concentrations (μg l -1 ) in drinking water sources across East Africa split by source type. Region Count Min Median Mean Max Region Count Min Median Mean Max Abeshege 12 2 5.35 6.48 18 Luwero 10 8 12.5 43.9 313 Balaka 12 3.2 20 40.1 165 Machinga 11 2.7 6.8 12 61 Budaka 11 1.6 6 10.2 29 Mecha 12 0.35 0.92 0.884 1.9 Ejere 8 2.5 7.1 16 57 Nkhotakota 16 2.2 3.75 5.64 16 Kobo 26 2.08 13.1 49.4 322 Oyam 13 0.3 2.5 3.64 9.6 Kumi 16 1.2 32.5 43.2 115 Singida 15 10 77 161 470 Lay Gayint 27 2.8 8.58 11.2 62.8 Sodo 12 0.77 5.8 9.23 30 Lilongwe 8 1.3 2.95 5.79 24 Tabora 45 2.1 46 81.2 718 Table 2 Summary statistics for iodine concentrations (μg l -1 ) in drinking water sources in regions of Ethiopia, Uganda, Tanzania and Malawi. 0.0 2.5 5.0 7.5 As μgL 0 1000 2000 3000 4000 Sr μgL 0 5 10 15 20 U μgL 0 500 1000 1500 HCO 3 mgL 0 100 200 Ca mgL 0 100 200 Mg mgL 0 200 400 600 800 Na mgL 0 10 20 30 K mgL 0 500 1000 1500 Cl mgL 0 200 400 600 SO 4 mgL 0 20 40 60 70 80 Mo μgL 0 1.5 5 10 15 F mgL 300 200 100 0 I μgL 300 200 100 0 I μgL 300 200 100 0 I μgL Bedrock Basement Igneous Unconsolidated Figure 2 Groundwater sample locations included in the preliminary study. n = 12 8 26 27 12 12 n = 11 16 10 13 n = 15 45 n = 12 8 11 16 UGANDA TANZANIA ETHIOPIA MALAWI n = 11 *7 7 2 n = 5 **12 9 2

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  • Expert | Impartial | Innovative

    Emma Crewdson email: [email protected]

    Contact information

    Iodine in drinking water from East African groundwater sourcesE Crewdson1, P L Smedley1, and A M MacDonald21 British Geological Survey, Keyworth, Nottingham, UK 2 British Geological Survey, Edinburgh, UK

    BackgroundThe content of iodine in the diet has implications for human health. Chronic deficiency has long been associated with development of iodine-deficiency disorders (IDDs) including goitre. Drinking water, including groundwater, contributes to the dietary iodine intake so establishing the content and distribution in water improves the understanding of dietary sources. However, whilst the prevalence of IDDs is widely reported, iodine is rarely analysed during traditional groundwater health studies. There are also no regulations for either the minimum or maximum concentrations of iodine in drinking water.This study aims to review the distribution of iodine in groundwater-sourced drinking water supplies in areas of Ethiopia, Uganda, Tanzania and Malawi (sample sites shown in Figure 2, summary statistics in Table 1 and 2). The study aims to deduce the sources and mechanisms controlling iodine concentrations in each region.

    Iodine and other elements in groundwaterAn assessment of the relationships between iodine and other dissolved ions was conducted in order to deduce the processes contributing to iodine content. Preliminary results indicate that the concentration of iodine is related to other dissolved ions. Sulphate, uranium, strontium, sodium and fluoride show the strongest relationships with iodine (Figure 4), and are in line with the association between iodine and TDS.

    ImplicationsIodine content is not simply controlled by the composition of rain water; increases occur in catchments through interactions with rocks and soils. The controls on iodine concentration in drinking water supplies have implications for the dietary intake of iodine and can be particularly marked in isolated populations, where low iodine in groundwater is reflected in crops and livestock of the local area.

    Next StepsWork is ongoing to investigate the relationships between iodine and other solutes in the groundwater, and to build a database of groundwater in East Africa. The natural iodine concentrations of the groundwaters will be combined with additional rainfall and aquifer composition data. The results will provide information on the iodine intake of populations with groundwater-sourced drinking water. By characterising the environmental sources and processes behind the iodine content, the results will contribute to wider public health initiatives in the mitigation of iodine deficiency disorders.

    Figure 3 Boxplots show the distribution of iodine occurring in natural waters in two regions of Ethiopia. * HDW with iodine concentration of 322 μg l -1 excluded from plot, ** HDW with iodine concentration of 62.8 μg l -1 excluded from plot.

    Figure 4 Relationships are shown between iodine and other elements, grouped by bedrock type. WHO (2011) guideline values indicated, showing maximum recommended concentrations. There are no health-based guideline values for sodium, magnesium, calcium, chloride, sulphate, carbonate or strontium. All samples are below the WHO (2011) guideline value for arsenic (10 μg l -1) and uranium (30 μg l -1).

    ReferencesBell, R. (2019). Impact of the 2015/16 El Niño on rural water security in Ethiopia.

    World Health Organisation (2011). Guidelines for drinking-water quality, fourth edition.

    MethodsGroundwater sources including, springs, shallow boreholes and hand dug wells have been sampled by the British Geological Survey across East Africa (examples of sampled drinking water sources shown in Figure 1). The hydrochemistry data have been compiled into a database for iodine in groundwater from East Africa. Variation in detection limits from the ICP-MS analysis method were accounted for. The preliminary results presented here are based on the iodine content of water from 196 shallow boreholes (BH), 38 hand dug wells (HDW), 18 springs (SP) and 10 rainfall samples.

    Figure 1 Examples of a shallow borehole (top left), hand dug well (top right) and spring drinking water source (bottom left) in Ethiopia (Bell, 2019).

    Iodine contentThe iodine content of groundwater varies both between source type (Table 1) and regionally (Table 2). Iodine concentrations are lowest in rainfall and springs, and greatest in boreholes and hand dug wells in two regions where data are available (also demonstrated in Figure 3).

    Water Source

    Count Min Median Mean Max Water Source

    Count Min Median Mean Max

    Boreholes 196 0.3 9.65 37.2 718 Springs 18 2.8 5.56 9.66 44Hand dug wells 38 2.08 19.5 53.4 322 Rainfall 10 1.8 3.4 4.02 7

    Table 1 Summary statistics for iodine concentrations (μg l -1) in drinking water sources across East Africa split by source type.

    Region Count Min Median Mean Max Region Count Min Median Mean MaxAbeshege 12 2 5.35 6.48 18 Luwero 10 8 12.5 43.9 313Balaka 12 3.2 20 40.1 165 Machinga 11 2.7 6.8 12 61Budaka 11 1.6 6 10.2 29 Mecha 12 0.35 0.92 0.884 1.9Ejere 8 2.5 7.1 16 57 Nkhotakota 16 2.2 3.75 5.64 16Kobo 26 2.08 13.1 49.4 322 Oyam 13 0.3 2.5 3.64 9.6Kumi 16 1.2 32.5 43.2 115 Singida 15 10 77 161 470Lay Gayint 27 2.8 8.58 11.2 62.8 Sodo 12 0.77 5.8 9.23 30Lilongwe 8 1.3 2.95 5.79 24 Tabora 45 2.1 46 81.2 718

    Table 2 Summary statistics for iodine concentrations (μg l -1) in drinking water sources in regions of Ethiopia, Uganda, Tanzania and Malawi.

    0.0 2.5 5.0 7.5 As μgL

    0 1000 2000 3000 4000 Sr μgL

    0 5 10 15 20 U μgL

    0 500 1000 1500 HCO3 mgL

    0 100 200 Ca mgL

    0 100 200 Mg mgL

    0 200 400 600 800 Na mgL

    0 10 20 30 K mgL

    0 500 1000 1500 Cl mgL

    0 200 400 600 SO4 mgL

    0 20 40 60 70 80Mo μgL

    0 1.5 5 10 15F mgL

    300

    200

    100

    0

    I μgL

    300

    200

    100

    0

    I μgL

    300

    200

    100

    0

    I μgL

    Bedrock

    BasementIgneousUnconsolidated

    Figure 2 Groundwater sample locations included in the preliminary study.

    n = 12

    8

    26

    27

    1212n = 11

    16

    1013

    n = 15

    45

    n = 12

    811 16

    UGANDA

    TANZANIA

    ETHIOPIA

    MALAWI

    n = 11 *7

    7 2

    n = 5 **12

    9

    2