Al-Diwaniyah City is one of Iraq provinces and branch of Euphrates pass through the city and divided it into two banks. Five local water treatments stations were selected due to their high rate production and due to the fact that most people in the city of Al-Diwaniya/Iraq are using the water for drinking purposes from these stations. These units are use the treated water from the water treatment plants and treat it with the (RO) system and then filled the plastic bottles in a size of 20 and 10 litres. Samples were collected between February and April 2015. Samples were collected in a polyethylene 1 liter bottles and transferred in a cooling box to the laboratory in Al-Qadisiyah Environmental Authority for analysis. The sampling regime was once a week for seven weeks from the selected five local water treatment units. The parameters were measured are Ca, Mg, TH (Total Hardness), PH, EC (Electrical Conductivity), and TDS (Total Dissolved Solids). Results were tabulated and analyzed using simple descriptive statistics. Independent T-test for two means and analysis of variance for multiple means were used. P ≤ 0.05 were considered significant throughout data analysis.

The method for determination of Total hardness, calcium, and magnesium depend on the titration with EDTA (Ethylene diamine tetra acetic acid) which is followed the (APHA) [20] . For total hardness, about 50 ml of the water sample was transferred to the conical flask, then 2 - 3 ml of the buffer (pH 10) solution. Followed by adding Eriochrome Black T to the contents of the flask (add gradually to the flask, swirling after each addition) until a deep wine red color is obtained. Finally titrate the water sample with the EDTA until changing the color from the red to the dark blue.

For the determination of calcium, about 50 ml of the water sample was transferred to the conical flask, then 2 ml of sodium hydroxide solution in order to maintained PH between 12 - 13. Followed by adding 0.1 - 0.2 mg of ammonium purpurate indicator (murexide) to the water sample in the flask in order to turn the sample to the pink color, finally titrate the water sample with the EDTA until changing the color from the pink to the purple and the amount consumed of EDTA can be used in the calculations to find the calcium concentration. For the magnesium, the concentration can be quantified depends on the results of total hardness and calcium calculations.

The results of PH, EC, and TDS are shown in the Table 1. For PH values, it can be noticed that from the results of (RO) treatment systems at all local treatment stations show that although the PH value was the lowest mean, however, the results show no significant difference between these stations, since the mean average of PH value were ranging from (6.4 - 6.9) with an average of 6.7 with standard deviation of 0.2. However, the mean PH value for the station (S2) was the lowest among the selected stations. Figure 1 shows the PH values for these five stations for seven weeks.

For the electrical conductivity (EC), the mean values were about 255.6 μS/cm ranging from (26.0 - 372.8). The results show that there is a significant difference between the station (S2) and the other stations in terms of their EC values.

In terms of Total Dissolved Solids (TDS), the results demonstrate that the concentration of TDS ranging from (16.9 mg/l - 203.5 mg/l). The results show there is a significant difference between the station (S2) and other stations. Figure 2 shows the mean values of these stations for the Total Dissolved Solids and Electrical Conductivity values.

The results of Ca, Mg and TDS are shown in the Table 2. It can be seen that the results of (RO) treatment systems at all local treatment stations show that the mean of the (DW supply) which represent the raw water for these stations is about (359 mg/l) and the mean total hardness (TH) for the station (S2) was the lowest (high rate

of removal); however, there is a significant difference between (S2) and other stations except station (S1) which show no significant difference. Figure 3 shows the mean concentrations of total hardness for the selected stations during the period of study.

In terms of Ca and Mg, the mean concentrations of the drinking water supply which represent the source for these stations (before passing through the RO systems) were (90.3 mg/l) and (31.2 mg/l) for Ca and Mg respectively. Moreover, the results show that the concentration of Ca and Mg at station (S2) were the lowest among the selected stations, where the average concentrations were about 5.3 mg/l and 9.5 mg/l for Ca and Mg respectively. In addition, the results show that there is a significant difference between station (S2) and other stations for both Ca and Mg concentration.

In general, it can be noticed that the most mean concentrations of these constituent were lower than Iraqi (IQ STD) and WHO (WHO STD)drinking water standards and also lower than what they were in the previous publications although the influent for these station were (drinking water) were very close to the Iraqi Drinking wa-

ter standards. In addition, due to the reason that all five station have the same water quality (drinking water from the water treatment plant) as influent to these stations, it can be seen that although the station (S2) was the best station in terms of its ability to remove these constituents, however, it is the worst station among the selected station because the high rate removal efficiency and that maybe due to filtration rate and also might be the changing of the filters. Figure 4 and Figure 5 show the mean values of total hardness for the selected stations during the period of study.

Around the world and in many countries, many different researches have published and reported the effect of low intake of calcium and magnesium of human health and activities. They also reported the effect of low calcium and magnesium concentration in the water for the people who drink very soft water.

The study achieved by Yang et al. demonstrated that there is a significant protective effect of calcium intake from drinking water against colon cancer [21] , and also against gastric cancer [22] . While Yasui and his colleagues revealed that low calcium and magnesium concentrations in drinking water poses risk of muscle atrophy factor [23] .

The results presented by Yang et al. show that there is a significant protective effect of calcium intake from drinking water on the risk of death from acute myocardial infarction (AMI) [24] . Moreover, the results achieved by Chiu et al. demonstrated that there may be a significant protective effect of calcium intake from drinking water against the risk of death due to kidney cancer with a concentration level of about 35 mg/l and 11.2 mg/l for Ca and Mg respectively [25] . These values were in accordance with the results carried out in this study and also other studies such as the study achieved by Moyel et al. show that the mean concentration of Ca is ranging from 5.9 - 11.8 mg/l and from the range of (4.4 - 13.9) mg/l for Mg concentration [26] . Furthermore, Morr, et al. have shown that the results of calcium and magnesium are compatible to what this study found [27] .

In a simple comparison between the above researches and present study, it is clear that the concentration of Calcium, Magnesium, and Total hardness in the selected RO treatment station in Al-Diwaniyah City is lower than or in the same level of the concentrations in the researches mentioned above, which leads to the fact that there is a high degree of risk to expose to these kinds of diseases (which mean a link between low concentrations and human health). The other issue, when there is a risk from pollution with a specific contaminates in a specific are, then it can be controlled by many different ways, while due the wide speared of these (RO stations) not only in Al-Diwaniyah City, they are all over the Iraqi cities and towns which reflect a potential influence on a wide range of municipalities and towns from the risk of low levels of these constituents.