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. 2016 May 30;23(17):17664–17675. doi: 10.1007/s11356-016-6806-y

Table 2.

Summary of the estimates of the effect (RR) of chromium topsoil levels, categorised in quartiles, on mortality due to different tumour types, by sex

Cancer site Men Women
Unadjusted Adjusted Unadjusted Adjusted
RR 95 % CI RR 95 % CI RR 95 % CI RR 95 % CI
Buccal cavity and pharynx
 Approach A q2a 0.996 0.926–1.071 1.050 0.977–1.128 1.014 0.898–1.144 1.061 0.944–1.190
 q3 0.973 0.901–1.050 1.053 0.981–1.131 0.994 0.879–1.124 1.044 0.931–1.170
 q4 0.947 0.875–1.026 1.025 0.958–1.096 1.105 0.979–1.242 1.149 1.0361.274
 Trend testb 0.981 0.956–1.007 1.006 0.984–1.027 1.033 0.993–1.072 1.044 1.0101.078
 Approach B SPDEc 0.970 0.900–1.037 0.938 0.835–1.024 1.096 0.967–1.233 1.118 1.0031.250
Oesophagus
 Approach A q2a 0.949 0.883–1.020 0.932 0.867–1.002 0.945 0.798–1.120 0.942 0.796–1.115
 q3 0.883 0.818–0.953 0.889 0.827–0.955 0.993 0.838–1.177 1.021 0.867–1.203
 q4 0.947 0.875–1.025 0.954 0.891–1.021 1.220 1.0381.435 1.328 1.1461.544
 Trend testb 0.981 0.955–1.006 0.985 0.964–1.007 1.078 1.0221.137 1.115 1.0631.170
 Approach B PDE c 0.978 0.893–1.060 0.990 0.901–1.129 1.254 0.989–1.497 1.263 0.991–1.508
Liver
 Approach A q2a 1.104 1.0111.206 1.003 0.926–1.086 0.973 0.853–1.110 0.864 0.761–0.980
 q3 1.027 0.934–1.130 0.944 0.871–1.022 1.020 0.889–1.172 0.921 0.814–1.041
 q4 1.097 0.992–1.213 0.982 0.911–1.059 1.041 0.902–1.201 0.935 0.833–1.049
 Trend testb 1.021 0.989–1.055 0.990 0.967–1.014 1.017 0.971–1.066 0.989 0.953–1.026
 Approach B SPDEc 1.026 0.930–1.151 1.051 0.948–1.197 1.050 0.905–1.198 1.020 0.891–1.184
Larynx
 Approach A q2a 0.930 0.864–1.001 0.944 0.879–1.013 1.122 0.871–1.444 1.188 0.909–1.550
 q3 0.965 0.893–1.042 1.009 0.941–1.082 1.116 0.866–1.435 1.206 0.925–1.571
 q4 0.930 0.858–1.008 1.012 0.947–1.081 1.175 0.954–1.453 1.188 0.940–1.507
 Trend testb 0.982 0.957–1.008 1.011 0.990–1.032 1.049 0.982–1.121 1.048 0.974–1.127
 Approach B SPDEc 0.963 0.827–1.068 0.990 0.905–1.074 1.279 1.0401.567 1.295 1.0371.611
Pleura
 Approach A q2a 1.052 0.840–1.318 0.970 0.777–1.209 0.951 0.701–1.291 0.879 0.666–1.157
 q3 1.192 0.944–1.508 1.223 0.990–1.51 1.162 0.866–1.554 1.312 1.0201.686
 q4 1.099 0.856–1.408 1.046 0.854–1.282 1.273 0.961–1.690 1.239 0.989–1.557
 Trend testb 1.037 0.957–1.123 1.030 0.967–1.098 1.098 1.0021.203 1.103 1.0271.185
 Approach B SPDEc 1.182 0.891–1.515 1.201 0.915–1.746 1.474 1.1201.975 1.399 1.0741.871
Breast
 Approach A q2a 1.028 0.986–1.072 1.042 1.0031.081
 q3 0.992 0.949–1.036 1.015 0.977–1.053
 q4 1.007 0.961–1.054 1.045 1.0091.082
 Trend testb 0.998 0.984–1.013 1.011 1.0001.022
 Approach B SPDEc 0.972 0.927–1.022 0.976 0.934–1.020
Uterus
 Approach A q2a 0.989 0.930–1.051 1.022 0.963–1.086
 q3 0.991 0.930–1.055 1.031 0.971–1.094
 q4 1.046 0.982–1.113 1.089 1.0311.151
 Trend testb 1.016 0.996–1.037 1.029 1.0111.047
 Approach B SPDEc 1.079 1.0191.130 1.026 0.963–1.092
Kidney
 Approach A q2a 1.061 0.984–1.145 1.063 0.993–1.139 0.952 0.863–1.049 0.931 0.853–1.015
 q3 1.056 0.976–1.142 1.093 1.0211.170 0.964 0.872–1.065 0.990 0.908–1.077
 q4 1.026 0.945–1.113 1.034 0.969–1.103 1.005 0.911–1.108 0.990 0.917–1.070
 Trend testb 1.005 0.979–1.031 1.008 0.988–1.029 1.005 0.974–1.038 1.004 0.980–1.030
 Approach B SPDEc 1.009 0.926–1.095 1.005 0.929–1.083 0.981 0.887–1.081 0.980 0.880–1.077
NHL
 Approach A q2a 1.022 0.944–1.106 1.013 0.939–1.092 1.049 0.972–1.132 1.050 0.974–1.131
 q3 1.032 0.952–1.119 1.061 0.986–1.142 1.029 0.953–1.112 1.058 0.982–1.139
 q4 0.994 0.915–1.080 0.987 0.919–1.059 1.076 0.997–1.161 1.092 1.0181.170
 Trend testb 0.997 0.971–1.024 0.997 0.975–1.02 1.021 0.996–1.046 1.027 1.0051.050
 Approach B SPDEc 0.994 0.915–1.080 0.984 0.909–1.067 1.062 0.985–1.132 1.064 0.988–1.143

The table shows the results of the approaches A and B, broken down as follows: unadjusted (model n.1) and adjusted for socio-demographic variables and industrial emissions (model n.3)

aQuartiles: reference [6.46, 20.2], q2 [20.24, 25.0], q3 [24.99, 29.9] and q4 [29.86, 243.7 mg kg−1]

bRR, taking quartiles as a categorical variable

cRR for a change of one unit in the logarithm of the elements’ soil concentration