Ce
ment-based
materials play an i
mportant role in
multi-barrier concepts developed worldwide for the safe disposalof hazardous and radioactive wastes. Ce
ment is used tocondition and stabilize the waste
materials and to constructthe engineered barrier syste
ms (container, backfill, andliner
materials) of repositories for radioactive waste. In thisstudy, Ni uptake by hardened ce
ment paste has beeninvestigated with the ai
m of i
mproving our understandingof the i
mmobilization process of heavy
metals in ce
ment onthe
molecular level. X-ray absorption spectroscopy(XAS) coupled with diffuse reflectance spectroscopy(DRS) techniques were used to deter
mine the localenviron
ment of Ni in ce
ment syste
ms. The Ni-doped sa
mpleswere prepared at two different water/ce
ment ratios (0.4,1.3) and different hydration ti
mes (1 hour to 1 year) using asulfate-resisting Portland ce
ment. The
metal loadingsand the
metal salts added to the syste
m were varied (50up to 5000
mg/kg; NO
3-, SO
42-, Cl
-). The XAS study showedthat for all investigated syste
ms Ni(II) is predo
minantlyi
mmobilized in a layered double hydroxide (LDH) phase,which was corroborated by DRS
measure
ments. Only a
minor extent of Ni(II) precipitates as Ni-hydroxides(
![](/i<font color=)
mages/gifchars/alpha.gif" BORDER=0>-Ni(OH)
2 and
![](/i<font color=)
mages/gifchars/beta2.gif" BORDER=0 ALIGN="
middle">-Ni(OH)
2). This finding suggests thatNi-Al LDH, rather than Ni-hydroxides, is the solubility-li
miting phase in the Ni-doped ce
ment syste
m.