Notably, the EPA's cancer benchmark level for PCDD/Fs is three orders of magnitude higher than the WHO benchmark (which we applied to non-cancer endpoints), explaining why the cancer ratio of estimated risk to benchmark exceeds 100 while the non-cancer ratio of estimated hazard to benchmark is less than one.
Each month that your sales exceed a certain benchmark, you earn the bonus for that benchmark and any lower benchmarks exceeded during that month.
The number of benchmark concentrations exceeded by modeled concentrations ranged from 8to3232 per census tract, with a mean of 14.
The cancer benchmark risk ratios are shown in Figure 2 and indicate that the benchmarks were exceeded by all five contaminants for which there was a cancer benchmark (arsenic, dieldrin, DDE, PCCD/PCDFs and chlordane), in school-aged and preschool children.
These are essential to consider so that we are prepared for such conditions if the 1.5° and 2 °C benchmarks are exceeded.
Both analyses found that cancer benchmarks were exceeded for arsenic, chlordane, dieldrin, DDT/DDE, and dioxin among children.
Non-cancer benchmarks were exceeded by >95% of preschool-age children for acrylamide and by 10% of preschool-age children for mercury.
Dietary strategies to reduce exposure to toxic compounds for which cancer and non-cancer benchmarks are exceeded by children vary by compound.
All WHO benchmarks were exceeded except for "speed of drying" at visit 2, and "texture" at visit 2 and 3. Cumulative study time expenditure was 14 days for the observer and four days for participants.
Additional work is needed to estimate the frequencies at which air quality benchmarks are exceeded in the tens of millions of U.S. homes that have natural gas cooking burners.
(Thus, if you reach the level to earn a 25 percent bonus for a particular month, you also earn the bonuses for the 10, 15 and 20 percent benchmarks you exceeded that month).
