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Radon in groundwater Analysis of causes and development of a prediction methodology Skeppström K. PhD. Student Dept. of Land and Water Resources Engineering, KTH Layout of presentation Radon (focus of Rn in groundwater) Objective of project / Phases involved Methodology Results & Discussions Radon • Radioactive • Colourless, odourless, noble gas • Exists as 3 main isotopes: •222Rn (uranium decay series, 238U),Half-life ( T1/2) = 3.8 days •220Rn (Thorium decay series, 232Th), T1/2 = 56 seconds •219Rn (Actinium decay series, 235U), T1/2 = 4 seconds • Cancer risk • 500 cases of lung cancer/year in Sweden; smokers have a higher risk. • Risk of developing of other cancers ? Uranium decay series 238U (parent) 226Ra 214Po 234Th 234Pa 234U 230Th 222Rn 218Po 214Pb 214Bi + + 210Pb 210Bi 210Po 206Pb (stable) Principal cause of radon problem Geology Genomsnittlig årlig stråldos i Sverige Source: Statens Strålskyddsinstitut Exposure routes groundwater Construction material Soil gas / bedrock (Granite) Regulatory limits (Sweden) Radon in water Radon in air Radon > 1000 Bq/l Radon: 400 Bq/m3 Gränsvärde för otjänligt Riktvärde för radon i befintliga bostäder Radon > 100 Bq/l Radon: 200 Bq/m3 Gränsvärde för tjänligt med anmärkning Gränsvärde för radon i nya bostäder Radon problems in water Surface water Groundwater Dug wells Drilled wells (soil/sand aquifer) (Hard rocks) How radon in water is a problem? 1000 Bq/l in water 100 Bq/m3 in air Dish washing 95 % Shower 60 – 70 % Bath 30 – 50 % Washing machine 90 – 95 % Tap water 10 – 45 % WC 30 % Radon in water Prerequisites Presence of parent elements, 238U or 226Ra Radon emanated in mineral grain escape in the pore space Recoil Theory Transport mechanisms Pore space filled with water- Radon dissolves in the water Water extracted from drilled wells (fracture water) • Diffusion • Convection Dosimetry How is it a problem ? • 1000 Bq/l is dangerous Precipitation of 238U 234U, 230Th, 226Ra from water to surface of fracture Leaching of 238U and 234U Emanation of 222Rn Content of 238U in the rock: 10ppm Concentration of 222Rn in Bedrock: 0.33Bq/m3 rocks 222 Rn Concentration of 222Rn in groundwater: 5 milj Bq/m3 Radon Emanation Radium atom Radon atom Mineral grain Pore Radon risk in Sweden Groundwater radon risk map of Sweden (after Åkerblom & Lindgren, 1997) N N Radon content in wells in the county of Stockholm 20km (White areas have too few wells) 40km 0km 20km 40km 1000 Rn conc. (Bq/L) 0 to 100 100 to 500 500 to 1000 1000 to 64000 Rn (Bq/L) 0km Radon risk areas calculated using kriging. 500 100 0 (Knutsson & Olofsson, 2002) Any deduction? Granite types of rocks with high uranium concentration High radon concentration in water not always the case Hypothesis of project The hypothesis stipulates that the occurrence of radon from groundwater is governed by a number of well-defined factors ranging from: • Geological (bedrock, soil, tectonic structures, flow pattern and surrounding environment) • Chemical (oxidation reaction, other processes in water) • Topographical (difference in elevation and slope that determine flow pattern and renewal tendency and frequency) • Technical (withdrawal system & frequency which determine circulation as well as ventilation possibilities. Purpose of research Map processes and factors influencing radon content in groundwater Develop a prediction model, based on statistics, that can be used to determine areas at risk. Study area Phases of the project Phase 1 Using GIS and multivariate analysis of data to assess factors affecting radon concentration – REGIONAL LEVEL Phase 2 Phase 3 Detailed study at Ljusterö to determine spatial & temporal variation of radon concentrations due to a range of factors. LOCAL SCALE Development of risk prediction model Phase 1 1. Data collection from: Swedish National Land Survey (elevation and landuse data) Swedish Geological Survey, SGU (soil & bedrock geology, fractures, radiometric) Municipalities (data about wells and radon content) 2. Data transformation and extraction using ArcGIS and its spatial analyst function 3. Statistical analyses including multivariate analysis of data. Factors considered • Elevation Variables Derived factors • Soil geology • Altitude difference • Bedrock • Predominant soil, bedrock, landuse within a certain vicinity e.g. 200 m • Slope of the terrain • Fracture zone • Landuse • Uranium content Geographical Information System (GIS) • GIS is a computer system for managing spatial data. • Purpose of GIS • • • • • • Organisation Visualisation Spatial Query Combination Analysis Prediction Visualisations with GIS Bedrocks Soil What is my objective? For each well, relevant spatial patterns need to be extracted from the factor maps Data obtained in different formats, e.g ASCII, point vector GIS Software: ArcMap Spatial analyst function Geostatistical software To generate continuous surfaces with a spatial resolution of 50 m + Derive factors Ultra edit software Methodology using GIS Factors Data preparation Data extraction Raster format .. . .. . Topography wells Geology Pixel size: 50m x 50m Radiometric Landuse Continuous surface Database Wells X Y Rn Factor 1 Statistical methods • Which method? • Relate radon concentration with a large number of variables • Variables are both qualitative and quantitative in nature • Non-normal distribution of many variables • Use of covariance and correlations ? Careful with the interpretations • Not much information about association between variables • Non-linear associations can exist • Very sensitive to ‘ wild observations- outliers ’ Statistical Analyses Use of multivariate analysis of data – – – Each observational unit is characterised by several variables. It enables us to consider changes in several properties simultaneously Non normality of data (non parametrical tests) Statistical Methods 1. Analysis of variance 2. Principal Component Analysis (PCA) PCA method • Eigenvectors of a variance-covariance matrix • Linear combinations of these variables • Its general objectives: • Data reduction (A small amount of k components account for much of the variability of the data) • Interpretation (may reveals relationships that were not previously suspected) Results of statistical analyses Descriptive Statistics Statistic parameters Number of wells Minimum radon concentration (Bq/l) Maximum radon concentration (Bq/l) Mean radon concentration (Bq/l) Median value Variance Standard deviation 4439 4.0 63560 492 230 1505978 1227 Radon concentrations in Stockholm County Boxplot Median 25%-75% Non-outlier range ANOVA - Altitude Anova - Relative altitude ANOVA-Bedrock ANOVA- Fracture ANOVA - Soil ANOVA- Landuse ANOVA- Uranium Summary of results High radon concentration in drilled wells is related to: – Low altitude – Granite rocks – Close distance to fracture – When overlying geology is lera/silt – Infrequent use of wells (summer houses) – An overview of the terrain in the surrounding of the wells (flat or hilly) is also of interest in connection to groundwater flow tendencies and speed of flow. Risk Variable Method Preparation Phase (Expert system) Data collection Statistical analyses Expert assessment Selection of significant variables Operational phase (User Interface) Define study area Determination of risk values Determination of uncertainty values Suming up risk and uncertainty values Final Risk Evaluation Risk Variable Modelling (RVM) V1 x R1 + V2 x R2 + V3 x R3 + ……….+ Vn x Rn = FRV FRV = Final risk value • Where Vi= a risk value for a specific variable (-2 to +2) Ri = the rating of the variable (1 to 3) Ratings after RVM Altitude 2 Soil 2 Uranium 3 Landuse 2 Bedrock 3 Distance from fracture 3 An example of a risk map Field Studies Field studies at Ljusterö Why Ljusterö? • Number of wells = 198 • 141 wells exceeding 500 Bq/l (71%) • 96 wells exceeding 1000 Bq/l (48%) • Radon concentration • Mean = 1942 Bq/l • Minimum = 50 Bq/l • Maximum = 63560 Bq/l Wells on ljusterö predominant geology is gnejsgranitoid What was done? To choose 3-4 study areas on Ljusterö, exhibiting drastic fluctuations in the radon concentration and to perfom detailed study at these locations Detailed study • Analysis of geology (bedrock type, fracture zones, tectonic zones and fracture filling minerals, soil type and soil depth) • Altitude and other terrain considerations • Analysis of technical factors (wells technical design, hauling system, spatial temporal extraction patterns of wells) • Radiometric measurements of radiation (from soil around wells as well as measurements of radiation in wells and in tap water) • Chemical analyses in water samples (U, Ra, Rn, fluoride and other water components)