Page 201 - 00. Complete Version - Progress Report IPEN 2014-2016
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Nuclear Science and Technology | Progress Report  201





               tracers of marine processes, as ground water   increase of water column depth and ranged
               discharge. The activity concentrations of  Ra,   from 0.049 cm·y1 to 0.40 cm·y1.
                                                      226
               228 Ra and  Pb in four short marine cores, col-
                        210
               lected from the continental platform to up-    Radon as an indicator of environmental
               per slope of Southwest Atlantic Ocean, were    contamination by hydrocarbons in free-phase
               determined. Taking into account the results
               obtained, sedimentation rates and the ages
               of each sediment layer were determined us-
               ing the geochronological dating method with
               210 Pb. All sediment samples were totally ac-
               id-digested in microwave. The sequential ra-
               diochemical separation of  226 Ra,  228 Ra,  210 Pb
               were performed, obtaining in the end the pre-
               cipitation of Ba(Ra)SO4 and PbCrO4. The gross
               δ measurements of    226 Ra and gross δ mea-
                                      210
               surements of  Ra and  Pb from the precipi-
                            228
               tates were carried out in a gas-flow low back-
               ground proportional counter. Concerning all
               cores analyzed, the activities concentrations of
                                                              Figure 3. Map of isoconcentrations of 222Rn activity
               226 Ra ranged from 14 Bq·kg1 to 154 Bq·kg1; the   obtained with SSNTD detectors in winter.
                                228
               concentrations of  Ra ranged from 17 Bq·kg1
               to 45 Bq·kg1; and the concentrations of  210 Pb
               ranged from 20 Bq·kg1 to 2073 Bq·kg1. High     Contaminated sites by NAPL (Non-Aqueous
               values of  210 Pb were observed on the top of   Phase Liquids) may lead to safety risks to hu-
               all the cores studied, mainly related to atmo-  man health and to ecosystems, restrictions to
               spheric deposition. The results obtained in this   urban development and decrease of real es-
               work were of the same order of magnitude of    tate value. Radon gas as an indicator for the
               those reported in the literature available on   analysis of subsurface soil gas, once this noble
               non-contaminated areas of Southeast Brazil-    gas presents good solubility in a wide range of
               ian Coast. Sedimentation rates fall with the   NAPL, being partially retained in the NAPL con-
                                                              tamination, was used. Therefore, a decrease of
               Figure 2. Vertical profile (cm) of natural isotopes  Ra,  Ra, to-  the activity of radon in the contaminated soil
                                                  228
                                              226
               tal and unsupported (ns)  Pb concentrations (Bq·kg1) along   gas can be expected, due to the high capacity
                               210
               a short marine sedimentary profile in SW Atlantic Ocean.
                                                              of partitioning of radon in NAPL, which allows
                 Ra-226    Ra-228     Pb-210   Pb-210ns
                                                              that the NAPL retain part of the radon previ-
                0                                             ously available in the soil pores. The survey
                5
               20                                             was carried out at a disused industry, contam-
               25                                             inated by low volatile NAPL, located at south-
               20                                             east of São Paulo city, from June 2014 to May
               25                                             2015. Radon was evaluated by passive detec-
               30                                             tion methodology with CR39 solid state nucle-
               35                                             ar track detectors (SSNTD) in ten monitoring
               40
                                                              stations installed in the contaminated area
               45
                 0        250       500       750      1000   investigated and named “A” to “J”. Radon con-
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