## 3 Results and Discussion
### The Assessment of Health Risk-Sediments
#### 3.3.2 Hazard Quotient (HQ) and Hazard Index (HI)
\begin{table}
\begin{tabular}{c c c c c c c c} \hline \hline \multirow{2}{*}{\
\begin{tabular}{c} **Sampling** \\ **Sites** \\ \end{tabular} } & \multirow{2}{*}{
\begin{tabular}{c} **Toxic Metals** \\ **[mg/kg]** \\ \end{tabular} } & \multicolumn{2}{c}{**ADDing [mg/kg]**} & \multicolumn{2}{c}{**ADDinh [mg/kg]**} & \multicolumn{2}{c}{**ADDderm [mg/kg]**} \\ \cline{3-8}  & & **Children** & **Adults** & **Children** & **Adults** & **Children** & **Adults** \\ \hline \multirow{8}{*}{S1} & Cr & \(7.30\times 10^{2}\) & \(3.13\times 10^{2}\) & \(5.25\times 10^{-1}\) & \(2.25\times 10^{-1}\) & \(4.09\times 10^{0}\) & \(6.24\times 10^{0}\) \\ \cline{2-8}  & Pb & \(5.69\times 10^{1}\) & \(2.44\times 10^{1}\) & \(4.10\times 10^{-2}\) & \(1.76\times 10^{-2}\) & \(3.19\times 10^{-1}\) & \(4.87\times 10^{-1}\) \\ \cline{2-8}  & Zn & \(2.27\times 10^{2}\) & \(9.71\times 10^{1}\) & \(1.63\times 10^{-1}\) & \(6.99\times 10^{-2}\) & \(1.27\times 10^{0}\) & \(1.94\times 10^{0}\) \\ \cline{2-8}  & Cu & \(2.55\times 10^{2}\) & \(1.09\times 10^{2}\) & \(1.83\times 10^{-1}\) & \(7.86\times 10^{-2}\) & \(1.43\times 10^{0}\) & \(2.18\times 10^{0}\) \\ \cline{2-8}  & Fe & \(3.28\times 10^{4}\) & \(1.40\times 10^{4}\) & \(2.36\times 10^{1}\) & \(1.01\times 10^{1}\) & \(1.84\times 10^{2}\) & \(2.80\times 10^{2}\) \\ \hline \multirow{8}{*}{S2} & Cr & \(2.32\times 103\) & \(9.94\times 10^{2}\) & \(1.67\times 10^{0}\) & \(7.15\times 10^{-1}\) & \(1.30\times 10^{1}\) & \(1.98\times 10^{1}\) \\ \cline{2-8}  & Pb & \(1.46\times 10^{2}\) & \(6.24\times 10^{1}\) & \(1.05\times 10^{-1}\) & \(4.49\times 10^{-2}\) & \(8.16\times 10^{-1}\) & \(1.25\times 10^{0}\) \\ \cline{2-8}  & Zn & \(2.79\times 10^{2}\) & \(1.20\times 10^{2}\) & \(2.01\times 10^{-1}\) & \(8.60\times 10^{-2}\) & \(1.56\times 10^{0}\) & \(2.38\times 10^{0}\) \\ \cline{2-8}  & Cu & \(2.91\times 10^{2}\) & \(1.25\times 10^{2}\) & \(2.09\times 10^{-1}\) & \(8.97\times 10^{-2}\) & \(1.63\times 10^{0}\) & \(2.49\times 10^{0}\) \\ \cline{2-8}  & Fe & \(4.42\times 10^{4}\) & \(1.89\times 10^{4}\) & \(3.18\times 10^{1}\) & \(1.36\times 10^{1}\) & \(2.47\times 10^{2}\) & \(3.78\times 10^{2}\) \\ \hline \multirow{8}{*}{S3} & Cr & \(1.03\times 10^{2}\) & \(4.39\times 10^{1}\) & \(7.38\times 10^{-2}\) & \(3.16\times 10^{-2}\) & \(5.74\times 10^{-1}\) & \(8.77\times 10^{-1}\) \\ \cline{2-8}  & Pb & \(4.31\times 10^{1}\) & \(1.85\times 10^{1}\) & \(3.10\times 10^{-2}\) & \(1.33\times 10^{-2}\) & \(2.41\times 10^{-1}\) & \(3.68\times 10^{-1}\) \\ \cline{1-1} \cline{2-8}  & Zn & \(1.46\times 10^{2}\) & \(6.27\times 10^{1}\) & \(1.05\times 10^{-1}\) & \(4.51\times 10^{-2}\) & \(8.19\times 10^{-1}\) & \(1.25\times 10^{0}\) \\ \cline{1-1} \cline{2-8}  & Cu & \(2.40\times 10^{2}\) & \(1.03\times 10^{2}\) & \(1.73\times 10^{-1}\) & \(7.40\times 10^{-2}\) & \(1.34\times 10^{0}\) & \(2.05\times 10^{0}\) \\ \cline{1-1} \cline{2-8}  & Fe & \(2.11\times 10^{4}\) & \(9.03\times 10^{3}\) & \(1.52\times 10^{1}\) & \(6.50\times 10^{0}\) & \(1.18\times 10^{2}\) & \(1.80\times 10^{2}\) \\ \hline \hline \end{tabular}
\end{table} 
Table 8: ADD values [mg/kg] for the sediments at all the studied sites: S1 “Blekitma Laguna”, S2 “Huta”, and S3 “Mala Szwecja”. work of [PERSON] et al. [56], the highest values for HQ and HI were recorded in soil for Cr, but they were not greater than 1, which is also the case in our studies.