Abstract
INTRODUCTION
According to the Linear No Threshold hypothesis of radiation damage (LNT) lifespan decrease (or cancer or mutation risk) remains linear as the dose of radiation goes to zero. Data used by the National Academy of Sciences (U.S. National Research Council Committee to Assess Health Risks from Exposure to Low Level of Ionizing Radiation 2006) (Figure 1) are consistent with this hypothesis, but the error bars are so large that this data might just as well support a threshold.

Excess Solid Cancer Risk vs. Radiation Dose, redrawn from original figure published in (U.S. National Research Council Committee to Assess Health Risks from Exposure to Low Level of Ionizing Radiation 2006). Note 1 Sv = 1 Gy.
Although it is reasonable to assume that radiation damage to DNA and other cellular machinery is linear as a function of radiation dosage (as has been used in development of radiation protection standards), actual damage is mitigated by cellular repair mechanisms. These repair mechanisms probably increase initially, then reach a maximum so that, depending on parameters, various non-linear curves are possible. It may even be that there is a protective effect due to increased damage response to small amounts of radiation or other types of biological stress.
The goal of this paper is to investigate the biological effects of radiation using
RESULTS
Demography Experiment
A demography experiment was done, as detailed in the methods section. Adult flies were irradiated at age 24–48 hours post-eclosion with incident radiation levels 1 ranging from 0 to 400 J/kg. The results of the demography experiment are shown in Figure 2 and Table 1, as well as supplemental Figure S1. We did not detect any significant difference among the lifespans of flies exposed to radiation less than or equal to 50 J/kg (based on log rank test results, shown in supplemental Tables S2 and S3). However, flies exposed to 100 J/kg or more showed a statistically significant reduction in lifespan compared to controls. Larger incident radiation levels increased the magnitude of the reduction in lifespan. Hence, this result is consistent with a threshold effect on mortality. These results were confirmed by a second demography experiment (shown in supplemental Figure S1 and supplemental Table S1), which we refer to as replicate 2 (to distinguish it from the replicate 1 demographic studies presented in this section).

Survivorship curves for the demography experiment. Incident radiation levels less than or equal to 50 J/kg show no statistically significant differences from control; incident radiation levels greater than or equal to 100 J/kg show a statistically significant difference from control.

Comparison of demography data with Baxter and Blair (1967a) suggests absorbed dose as a more appropriate measure of radiation than incident radiation level. The demography experiment featured in the results section is referred to as replicate 1 and the second experiment is referred to as replicate 2. (A) Comparison of incident radiation level. (B) Comparison of absorbed dose. (C) Data from (B), with log of absorbed dose shown.

Supplemental demography data. (A) Survivorship curves for replicate 2. (B) Mortality rate data for replicate 1. (C) Mortality rate data for replicate 2. Mortality rates were calculated by the R packages
Median and maximum lifespan data.
Number of differentially expressed genes. High counts in 100 and 200 J/kg correspond with lifespan reduction in demography results, low counts in 10 and 50 J/kg correspond with no statistically significant change in demography results.
Summary of overrepresented KEGG functional pathways. Blue pathways were overrepresented in genes up-regulated from control, red pathways were overrepresented in genes down-regulated from control. The full list of KEGG pathways is available in supplemental Table S4.
Median and 90th percentile lifespan results for replicate 2.
Log rank test results for replicate 1.
Log rank test results for replicate 2.
Overrepresented KEGG pathways.
Mean lifespan for each radiation dose in replicates 1 and 2.
In demography analysis, it is important to consider the mortality rate (Tatar 2005). To further demonstrate the differences between mortality curves for different dosages, we fit the Gompertz-Makeham model of mortality (Makeham 1860) to our data. The results, shown in supplemental Figure S2 and discussed in Appendix 1, support the existence of a threshold behavior at incident radiation levels less than or equal to 50 J/kg.

Gompertz-Makeham mortality (Makeham 1860) fits. (A) Slopes of Log Mortality Rate Fits. The results are consistent with a threshold at 50 J/kg incident radiation level. (B) Intercepts of Log Mortality Rate Fits. The results generally show an earlier start of death at the highest doses of radiation. The variability is likely caused by the fact that the survival curves for the highest doses of radiation in replicate 2 are not exponential (Gompertz-Makeham model (Makeham 1860)) curves-however, these doses are well past the threshold dose. (C) Logarithm of time-independent parameter L in the Gompertz-Makeham mortality (Makeham 1860) fits. (D) Gompertz-Makeham mortality (Makeham 1860) fits for replicate 1. (E) Gompertz-Makeham mortality (Makeham 1860) fits for replicate 2. The demography experiment featured in the results section is referred to as replicate 1 and the second experiment is referred to as replicate 2.
Gene Expression Results
An RNA-sequencing gene expression experiment was performed as described in the methods section. Differentially expressed genes (genes with a statistically significant change in gene expression from control) were determined for each dose of radiation at each days 2, 10 and 20 following irradiation. Gene expression measurements were made for each dose (including control) at each time point, and every measurement had 3 replicates.
The number of differentially expressed genes compared to control in each combination of radiation dose and time point is shown in Table 2. The names of these genes are given in tabs 1–12 of supplemental dataset S1.
These results are consistent with the following conclusions:
The large number of genes changing at days 10 and 20 after incident radiation levels of 100 and 200 J/kg, paired with the lifespan results, suggest a state where the fly is irreparably damaged by the radiation. 1382 genes are in all four of these conditions, which is an 88 percent overlap.
The relatively small number of changes at incident radiation levels of 10 and 50 J/kg at all time points suggests that any damage caused by radiation has been limited and by day 20 has been repaired.
The results for 0.1 J/kg might be an anomaly. It is also possible that it is consistent with a protective effect, such as the effect reported by Seong et al. (2011).
Only a small number of genes change at day 2 in incident radiation levels larger than 0.1 J/kg. This suggests that the effects seen at later days could be due to chronic effects of oxidative stress, possibly from continuous generation of reactive oxygen species as described in Azzam et al. (2012).
In 100 and 200 J/kg at days 10 and 20, the vast majority of differentially expressed genes are down-regulated from control. This is consistent with damage to DNA, possibly from reactive oxygen species generated from the radiation's radiolysis effect on cellular water or mitochondrial DNA translocating to the nucleus (Azzam et al. 2012).
The physiological functions associated with changes in gene expression can be determined using a database of known functions of genes. The significant genes shown in Table 2 were compared to the functional pathway database of the Kyoto Encyclopedia of Genes and Genomes (KEGG) (Kanehisa and Goto 2000; Kanehisa et al. 2012), and the over-represented pathways were computed. Table 3 summarizes the result, and supplemental Table S4 contains the full lists of overrepresented functional pathways. The physiological functions associated with changes include oxidative phosphorylation (oxphos), metabolism of antioxidants and sugars, repair/protein turnover and signaling. These functions are consistent with a response to oxidative damage; this idea is presented in more detail in the discussion section.
Measuring Radiation Dosage
We compare our data with the data in Table I from Baxter and Blair (1967a), another demography experiment with a wide range of incident radiation levels ranging from control to 164,000 Roentgens (approx. 1,640 J/kg). Baxter and Blair's (1967a) experiments and our experiments were done using different gamma ray sources. Baxter and Blair (1967a) used Cobalt-60, which emits photons of 1.17 and 1.33 MeV. We used Cesium-137, which emits photons of 0.66 MeV.
On the surface, our data and Baxter and Blair's (1967a) lifespan results seem to be very different, as evidenced in Figure 3A. However, these two results can be reconciled if we model radiation damage in terms of absorbed dose, instead of the incident radiation level.
For both data sets, we estimated the absorbed dose for each incident radiation level (calculation in Appendix 1). We also scaled the age of death in each dose by the age of death in control flies, or the lowest incident radiation level available in replicate 2 (0.1 J/kg). Figure 3B shows the data from both of our demography experiments with the data of Baxter and Blair (1967a) with the incident radiation levels converted into absorbed doses. Figure 3C shows the result of Figure 3B with the absorbed dose in log scale. The data look consistent, and the shape of Figure 3C resembles Marion Lamb's log-linear/threshold model of radiation damage (Lamb and Smith 1969).
Comparison of Gene Expression Results with Existing Results
The gene expression data of Seong et al. (2011) probably allows the closest comparison to our data.
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Seong et al. (2011) found roughly 13% of the genome to be differentially expressed with low dose radiation, with 39 of the changing genes related to aging. They use male flies, 35 days old, whole body tissue, Oregon-R background, irradiated as eggs with 0.2 Gy of Cs-137 radiation. 35 days versus 3–22 days of age is an important difference in methodology, as is irradiation as an egg versus irradiation as an adult fly. The 1,818 differentially expressed genes in their experiment show a statistically significant overlap of 21 genes between genes up-regulated from control in their experiment and genes up-regulated from control in our data for 0.1 J/kg incident radiation level at day 2. The bioconductor package
DISCUSSION
Our experiments indicate a threshold effect in response to radiation for
Other laboratories have claimed a protective effect with low doses of radiation (Strehler 1962; Sacher 1963; Lamb 1964; Noethel 1965; Vaiserman et al. 1999; Vaiserman et al. 2003; Vaiserman et al. 2004a; Vaiserman et al. 2004b; Ogura et al. 2009; Moskalev et al. 2011; Seong et al. 2011). Of the studies in that group that present lifespan results, several of these are not comparable to our results. This is due to the irradiation being done at larval stages (Vaiserman et al. 2004b; Moskalev et al. 2011; Seong et al. 2011) or because the experimental conditions were known to be suboptimal (Strehler 1962; Noethel 1965). The results of Gowen and Stadler (1952) seem to support our results, finding a threshold effect in x-rays at dose 12,000 R (approximately 120 J/kg incident radiation level). Another data set from Baxter and Blair (1967a) also support our findings, with a threshold in Co-60 gamma rays at doses 6,800 and 13,700 R (approximately 68 and 137 J/kg incident radiation level). The one data set with comparable methods and a surprisingly different result is the 1963 data set of Sacher (1963), who finds a lifespan extension at doses of 1,500 to 3,000 R (approximately 15 to 30 J/kg incident radiation level) per day (median lifespan of order 40 days) with a 200 kv x-ray machine. Perhaps the difference is due to Sacher's use of daily irradiations instead of our one time irradiation (Sacher 1963).
In our gene expression results, many of the over-expressed pathways in 0.1 J/kg incident radiation level at day 2 show up in the opposite direction in the higher doses. This would be consistent with functions going from protective to harmful as the radiation dose crosses the threshold. The gene expression results do not seem to suggest a significant difference between control and 10 J/kg. Finally, there is a small but statistically significant overlap between 0.1 J/kg incident radiation level at day 2 and the data of Seong et al. (2011). Our data seem to be consistent with the existence of a protective effect, but are not conclusive. It is tempting to speculate that one may see a protective effect in other measures such as behavior.
The physiological responses inferred from our gene expression study (Table 3) are consistent with the oxidative theory of radiation damage (Bokov et al. 2004; Azzam et al. 2012): radiation damages cells by creating reactive oxygen species and other oxidizing agents that damage cell components, in addition to direct damage from the radiation. Perturbations in oxidative metabolism, including oxidative phosphorylation (oxphos) are a known effect of oxidative damage and are associated with chronic inflammation (Azzam et al. 2012). Metabolism of antioxidants is a direct response to oxidizing agents. Vitamins A, B1 and C have been found to have antioxidant properties (Olson 1996; Padayatty et al. 2003; Depeint et al. 2006). Mitochondria are a major target for reactive oxygen species (Azzam et al. 2012); and B vitamins, including vitamin B5, aid the function of mitochondria (Depeint et al. 2006). Reactive oxygen species are known to destroy sugars (Azzam et al. 2012) and amino acids (Stadtman and Levine 2003), which could affect the metabolism and production of sugars and amino acids as well as glycans, which are a type of sugar. Both the pentose phosphate pathway and carbon metabolism are regulated by the reactive oxygen species sensor ATM (Kruger and Ralser 2011); and purine is a known product of the pentose phosphate pathway. The peroxisome is known to have a role in the metabolism of reactive oxygen species (Bonekamp et al. 2009). Reactive oxygen species have been linked to signaling pathways, including Jak-STAT, Wnt and FoxO signaling (Bartosz 2009).
These oxidative damage responses are almost all seen at days 10 and 20 after level to 100 and 200 J/kg incident radiation, which correspond to the doses in which lifespan is decreased from control. Much of the response is also seen at day 10 after irradiation with 10 and 50 J/kg incident radiation levels; however, the responses are not seen at day 20, suggesting a recovery from the oxidative damage. This is consistent with the threshold effect in lifespan seen at incident radiation levels less than or equal to 50 J/kg. As discussed in Table 2, very few changes are seen at day 2 in any of these four doses, with most of the changes at day 2 related to sugar metabolism - perhaps the sugar destruction happens quickly and forces the metabolism of sugar to decrease initially from lack of availability. Much of the above radiation responses are seen in the lowest dose (0.1 J/kg incident radiation level) at day 2 after irradiation. However, the effects are seen in genes changing in the opposite direction from the other four doses, except for oxidative phosphorylation, which is in the same direction. This could be consistent with a protective response in the lowest dose at day 2. No effect is seen at days 10 and 20 with 0.1 J/kg incident radiation level.
Many questions remain to be answered. Among these: How does one convert from radiation damage levels in
In spite of the uncertainties, our results provide a strong indication of a very important effect: they contradict the linear no threshold hypothesis (U.S. National Research Council Committee to Assess Health Risks from Exposure to Low Level of Ionizing Radiation 2006).
MATERIALS AND METHODS
Radiation Doses
Two experiments were done. The experiment featured in the results section is called replicate 1, and the second experiment is called replicate 2.
In replicate 1, a demography experiment was done for incident radiation levels (in J/kg) background; 0.1; 1; 10; 50; 100; 200 and 400. The demography for 1 J/kg was an irregular shape and was ignored in the analysis. The gene expression experiment was done concurrently and included three replicates each of background; 0.1; 10; 50; 100 and 200 J/kg at days 2, 10 and 20 after irradiation.
In replicate 2, a demography experiment was done for incident radiation levels (in J/kg) 0.1; 1; 10; 100; 200; 400; 600; 800 and 1,000. The demography for 200; 400; 600 and 800 J/kg were started one week after the other doses.
In the demography data, day 1 was the collection of flies and day 2 was the day of irradiation.
Flies Used
Flies used were all male flies of the Canton-S genetic background. In replicate 1, approximately 300 flies were used for each radiation dose (10 vials of 30–32 flies each, before escapes). In replicate 2, approximately 90–120 flies were used for each radiation dose (3–4 vials of 30–32 flies each, before escapes). All flies were kept in a humidified (50%), temperature-controlled incubator with 12 hour on/off light cycle at 25 °C in vials containing standard cornmeal medium, as in Bauer and Antosh et al. (2010). Flies were collected under light anesthesia (carbon dioxide) and randomly divided into treatment groups.
Irradiation methods
Flies were irradiated at the Brown University Irradiator, a Cesium-137 gamma ray source 4 . Exposure rate values were taken in Roentgens (see footnote 1) from initial values given by the manufacturer, corrected for decay, and verified biannually with ion chamber measurements.
Exposure rates varied by 1.2 percent for incident radiation levels greater than or equal to 1,000 R (10 J/kg) because of decay of the radiation source between experiments. We used different exposure rates for the 1 and 10 J/kg incident radiation levels (100 R and 1,000 R) because of the lower limit of exposure time accuracy in the irradiator. However, the longest of these irradiations was 2.77 minutes. The exposure rates changed due to varying the distance between the fly vials and the source.
In replicate 1, the exposure rates and times were 0.1 J/kg (10 R): 0.02 min at 590.6 R/min; 1 J/kg (100 R): 0.17 min at 590.6 R/min; 10 J/kg (1,000 R): 0.70 min at 1435.2 R/min; 50 J/kg (5,000 R): 3.48 min at 1435.2 R/min; 100 J/kg (10,000 R): 6.97 min at 1435.2 R/min; 200 J/kg (20,000 R): 13.93 min at 1435.2 R/min; 400 J/kg (40,000 R): 27.87 min at 1435.2 R/min. Background radiation flies were brought without food to the irradiation room while other flies were irradiated. All samples except 400 J/kg were irradiated between approx. 8:30 – 11:15 am; 400 J/kg was irradiated between approx. 1:30 – 4:00pm.
In replicate 2, the exposure rates and times were 0.1 J/kg (10 R): 0.28 min at 36.1 R/min; 1 J/kg (100 R): 2.77 min at 36.1 R/min; 10 J/kg (1,000 R): 0.69 min at 1452.4 R/min; 100 J/kg (10,000 R): 6.89 min at 1452.4 R/min; 200 J/kg (20,000 R): 13.78 min at 1451.6 R/min; 400 J/kg (40,000 R): 27.56 min at 1451.6 R/min; 600 J/kg (60,000 R): 41.53 min at 1451.6 R/min; 800 J/kg (80,000 R): 55.11 min at 1451.6 R/min; 1,000 J/kg (100,000 R): 68.85 min at 1452.4 R/min. All samples were irradiated between 1:00 and 4:00 pm.
Food was not irradiated. The flies were provided with water, which was injected into the vial stopper. Flies were irradiated at age 24–48 hours.
Demography Analysis
The R packages
RNA Sequencing
Flies were aged 2, 10 and 20 days after irradiation, then collected using light anesthesia and frozen using liquid nitrogen. Flies were stored at −80 degrees C until processed for sequencing. Sequencing library preparation was performed using the Illumina TruSeq protocol. Samples were multiplexed, 6 samples per lane, and run on an Illumina HiSeq 2000.
Gene Expression Analysis
Samples were aligned using Tophat (version 2) (Trapnell et al. 2009). Analysis was performed using the statistical programming language R (R Core Team 2012) and the open source software project Bioconductor (Gentleman et al. 2004). Gene counts were determined using the bioconductor package
Availability of Gene Expression Data
The gene expression data is submitted to the Gene Expression Omnibus repository, with accession number GSE47999.
Comparison of Demography Data
We compared with the data from Table I in Baxter and Blair (1967a). We only compared with the data points where the flies were irradiated on day 1, and if there were multiple experiments in the Baxter and Blair (1967a) dataset for a given dose we averaged the results (which were different by 0.3 days at the most). Baxter and Blair (1967a) only give average age of death, so we used average age of death in the comparison.
Comparison of Gene Expression Data
Differentially expressed genes from Seong et al. (2011), Moskalev et al. (2011) and Ogura et al. (2009) were translated to flybase ID numbers using flybase (McQuilton et al. 2012). Genes or probes that had 0 or >1 flybase ID references were not used in the comparison. Fisher's Exact Test was used to calculate the statistical significance of overlaps, with an estimate of N=15,000 total genes in
Unused Gene Expression Samples
The samples for incident radiation level 1 J/kg in the full experiment were never processed because the lifespan curve looked irregular. The samples for incident radiation level 400 J/kg were never processed because the high radiation effect was clear by 200 J/kg. One sample from control at day 20 after irradiation failed quality check and was discarded.
