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J Am Stat Assoc. Author manuscript; available in PMC 2010 April 13.

Published in final edited form as:

J Am Stat Assoc. 2007 January 1; 102(480): 1212–1220.

PMCID: PMC2853781

NIHMSID: NIHMS33428

See other articles in PMC that cite the published article.

Animal carcinogenicity studies, such as those conducted by the U.S. National Toxicology Program (NTP), focus on detecting trends in tumor rates across dose groups. Over time, the NTP has compiled vast amounts of data on tumors in control animals. Currently, this information is used informally, without the benefit of statistical tests for carcinogenicity that directly incorporate historical data on control animals. This article proposes a survival-adjusted test for detecting dose-related trends in tumor incidence rates, which incorporates data on historical control rates and formally accounts for variation in these rates among studies. An extensive simulation, based on a wide range of realistic situations, demonstrates that the proposed test performs well in comparison to the current NTP test, which does not incorporate historical control data. In particular, our test can aid in interpreting the occurrence of a few tumors in treated animals that are rarely seen in controls. One such example, which motivates our work, concerns the analysis of histiocytic sarcoma in the NTP’s 2-year cancer bioassay of benzophenone. Whereas the occurrence of three histiocytic sarcomas in female rats was not significant according to the current NTP testing procedure (P = 0.074), it was highly significant (P = 0.004) when control data from six recent historical studies were included and our test was applied to the combined data.

In accord with a mandate by the U.S. Congress, the NTP routinely evaluates the toxicity and carcinogenicity of various chemicals to which humans are exposed. The NTP has performed more than 500 long term rodent studies, involving over 450 chemicals, which has produced a rich collection of information about tumors in control animals. Often this database is used informally when assessing whether differences in tumor rates are dose-related, especially when tumors are rare, but a formal method of incorporating historical control data would be preferable.

As an example, the NTP recently conducted a two-year rodent bioassay to evaluate the toxicity and carcinogenicity of benzophenone, a chemical to which a large number of people are exposed (for details, see http://ntp.niehs.nih.gov). As is typical of NTP bioassays, both sexes of two rodent species were studied, with 50 animals randomly assigned to a control group and 50 to each of three dose groups for all four sex/species combinations. The results of standard analyses of histiocytic sarcoma in female rats were unsatisfying. The observed numbers of rats with this cancer were 0, 0, 1, and 2 in the control, low-dose, mid-dose, and high-dose groups. The usual trend test reported by the NTP was not statistically significant (P = 0.074) at the standard 5% level, but the NTP historical control database shows that spontaneous occurrences of this neoplasm are very rare. None of the 460 female rats among the control groups in 6 recent studies had a histiocytic sarcoma, yet 2 of 50 in the current high-dose group and 1 of 50 in the current mid-dose group developed this cancer. We are interested in determining if the trend in the benzophenone study is significant after formally taking into account that, historically, this tumor is extremely rare.

Over the past few decades, several methods have been proposed for including historical information in the analysis of current data. Many of the procedures focus on lifetime tumor rates and assume a beta-binomial model, which allows for extra-binomial variation among the tumor proportions from the historical control groups (see, for example, Tarone 1982; Yanagawa and Hoel 1985; Hoel and Yanagawa 1986; Tamura and Young 1986; Prentice et al., 1992; Ryan 1993). Similar approaches have been based on generalized binomial (Makuch et al., 1989) and logistic-normal (Dempster et al., 1983; Seewald 1994) models. A major disadvantage of these methods, however, is that they do not adjust for survival. When treatment a ects longevity, the time at risk for developing tumors can differ substantially across dose groups, in which case survival-adjusted procedures are necessary to avoid biases.

Generalizations have been suggested that account for survival, but they have various shortcomings of their own. For example, Ibrahim and Ryan (1996) proposed a Dirichlet-multinomial model that assumes tumors are rapidly lethal, while other methods are oriented toward nonlethal tumors (Ibrahim et al., 1998; Parise et al., 2001). Bayesian procedures have been developed that adjust for survival and do not make extreme lethality assumptions (Dunson and Dinse 2001; French and Ibrahim 2002), but these analyses require investigators to specify prior distributions and hyperparameters.

The need for a formal method of incorporating historical control data in the analysis of the current experiment has long been recognized (Haseman et al., 1984; Haseman 1995), but no procedure has emerged as the clear favorite (Greim et al., 2003). The Technical Reports Review Subcommittee of the NTP Board of Scientific Counselors, which includes two statisticians, has not endorsed any of the current methods and recommended a new procedure be developed for this important problem (http://ntp.niehs.nih.gov/files/TRRSMins0905.pdf). This article presents a new method which is relatively simple, incorporates historical control data, adjusts for survival, and avoids lethality restrictions and distributional assumptions. Section 2 describes the proposed statistical procedure and Section 3 reports the results of an extensive simulation study, which shows that our method has good operating characteristics. The proposed test is illustrated in Section 4 by applying it to two NTP data sets, and several concluding remarks are provided in Section 5.

Early procedures for analyzing carcinogenicity data, with or without incorporating historical control information, dealt with lifetime tumor rates. In general, though, methods should focus on age-specific tumor rates to avoid biases due to differential survival. Of the various age-specific rates, the most appropriate is tumor incidence (McKnight and Crowley 1984), which corresponds to the hazard function for time to tumor onset. As a function of age, the tumor incidence rate automatically adjusts for differential survival, and as the rate at which new tumors occur, it is a natural measure of carcinogenesis. Thus, we focus on the detection of a positive trend (across dose groups) in the age-specific tumor incidence rates.

Let *T* be the time to the first of two events, either tumor onset or death, and let *Y* (*t*) be an indicator that is 1 if the tumor is present at time *t* and 0 otherwise. The tumor incidence rate and the tumor-free death rate correspond to the event-specific hazard functions

and

respectively. Let π be the expected proportion of animals that develop a tumor during the study (i.e. the lifetime tumor rate), which can be expressed in terms of λ(*t*) and *β*(*t*):

(1)

where *t _{TS}* denotes the terminal sacrifice time (i.e. the length of the study).

Suppose there are *k* treatment groups in the current experiment, with associated dose levels *d*_{1} < *d*_{2} < < *d _{k}*, where animals in the first group are unexposed controls (

and

respectively, where at least one inequality in *H _{a}* is strict for at least one t. Equation (1) shows that tests oriented toward the {π

Suppose *n _{ci}* animals in the current study are randomized to the

Many early analyses used the linear trend test of Cochran (1954) and Armitage (1955) to compare lifetime tumor rates. Inferences based on lifetime rates can be misleading, though, if survival differs across treatment groups. For example, unless all animals live to the end of the study, the sample proportion *y _{ci+}*/

Bailer and Portier (1988) addressed the survival issue by defining a modified sample size , where *δ _{cij}* is a weight for animal

where , and the plus sign indicates summation over the missing index.

The usual Poly-3 trend test, with the Bieler-Williams variance adjustment, is

The NTP currently uses the following (conservative) variation of *W _{BW}*:

which shrinks *W _{BW}* toward 0. The continuity correction factor in the above formula is

where is a weighted average of the dose scores. In the absence of survival differences, *CF* reduces to half the largest difference between successive dose scores. Both *W _{NTP}* and

Peddada et al. (2005) suggested an alternative trend test which uses the Poly-3 weights, but does not assume the tumor rates are linear in dose, does not depend on the numerical scores assigned to the dose groups, and does not incorporate a continuity correction. Let denote the survival-adjusted isotonic regression estimate of π* _{ci}* (

The isotonic test statistic proposed by Peddada et al. (2005) can be written

which was motivated by a procedure that Williams (1977) derived to test the equality of normal means. Define *k* standard normal random variables: *Z _{i}* ~

where are the isotonized values of the {*Z _{i}*} using unit weights. Peddada et al. (2005) conducted extensive simulations which showed that their test generally was more powerful than the Bailer-Portier/Bieler-Williams test when comparing age-specific incidence rates, even though both tests are more naturally oriented toward the{π

Suppose there are *p* relevant studies in the historical control database, where this number depends on several factors. Generally, we would prefer to include only those historical studies for which the route of exposure (e.g. feed, gavage, inhalation, skin painting) is the same as in the current study. Also, we typically restrict our comparison to studies which were performed relatively recently, since background tumor rates are known to “drift” over time (Haseman, 1992). Thus, in practice, we anticipate incorporating control data from approximately 5 to 10 historical studies.

Let *n _{hm}* be the number of animals in the

The problem of detecting trends in tumor rates can be viewed as a special case of order restricted inference and can be solved by maximizing certain distances in a directed graph. Figure 1 shows a directed graph appropriate for the usual NTP situation, where there is a high-dose (HD) group, a mid-dose (MD) group, a lowdose (LD) group, a current control (CC) group, and a collection of historical control (HC) groups. The arrows indicate the restrictions that the tumor rates in the control groups do not exceed the rate in the low-dose group, which does not exceed the rate in the mid-dose group, which does not exceed the rate in the high-dose group. The control animals, both current and historical, are assumed to come from a common population, and thus there are no arrows connecting CC and HC.

Directed Graph Representing the Trends of Interest. The circles denote parameters in the historical control (HC) group, the current control (CC) group, the current low-dose (LD) group, the current mid-dose (MD) group, and the current high-dose (HD) group. **...**

In the spirit of Kolmogorov distance measures, we follow Peddada et al. (2001) and define a test statistic for the graph in Figure 1 as the maximum distance between connected points. Specifically, our test is *max*(*D*_{1}, *D*_{2}), where *D*_{1} is the distance between the current control group and current dose groups, and *D*_{2} is the distance between the historical control groups and current dose groups. Each of these two distances, *D*_{1} and *D*_{2}, is itself the maximum of two quantities. Distance *D*_{1} is the maximum of the Bieler-Williams version of the Poly-3 statistic and the order restricted inference statistic of Peddada et al. (2005) based on the current control group. Our choice for *D*_{1} was motivated by a test proposed by Peddada and Kissling (2006), who selected this pair of statistics because the former performs well against linear trends, while the latter performs well when trends are not linear. By taking the maximum of the two, we obtain a test with reasonably good power for detecting linear or nonlinear (but still non-decreasing) trends. Distance *D*_{2} has exactly the same form as *D*_{1}, except that it is based on the historical control groups rather than the current control group. Thus, the proposed test statistic is the maximum of four components. Two of the components are *W _{BW}* and

Our approach views the lifetime tumor rates in the current and historical control groups (π_{c1}, π_{h1}, … , π_{hp}) as random realizations from a common control population with mean π. If no animals die before the end of the study, the sample proportion *y*_{hm+}/*n _{hm}* has expected value π (

(2)

where σ^{2} is an unknown parameter that allows for extra-binomial variation.

Now suppose that some animals die before *t _{TS}* and we want to account for this by using Poly-3 adjusted sample sizes. Allowing for the random nature of the sample size in variance formula (2), we propose separate estimators for σ

and

The Bieler-Williams estimate of π(1 — π), say , is obtained by applying the formula for to the combined set of *p* historical control groups and *k* current groups. We estimate the variance of the Poly-3 adjusted tumor proportions in the current high-dose group, , and in the pooled historical control groups, , by

and

respectively, where . Note that although the extra binomial variation among the historical control groups should not extend to the current dose groups, we purposely inflate the estimated variance of by in the above formula to avoid the Behrens-Fisher problem. This modification leads to a slightly conservative test (described below), but we view it as a small price to pay for the resulting simplification.

Thus, we define a new pair of test statistics, say and , which are analogous to *W _{BW}* and

where are the isotonized values of {} under the constraint that π ≤ π_{c2} ≤ π_{c3} π* _{ck}*, with weights .

Finally, the proposed survival-adjusted test statistic for detecting a dose-related trend in the tumor rates, using both current and historical controls, is given by

Deriving the exact null distribution of *W* is not trivial. Hence we use critical values based on the approximations described below. In the next section, simulation studies reveal that our approximations control the Type I error rate very well.

Initially, assume that all animals survive to the end of the study and the lifetime tumor rates in all control and treated groups are equal to π. Also, let *v _{g}* denote the estimated variance of for

Denote the above limiting standard normal random variables by {*Z*_{0}, *Z*_{1}, … , *Z _{k}*}, where the first term (

We approximate the distribution of using the analogous function of *U*_{0}, *U*_{2}, … , *U _{k}*:

Both *W _{ISO}* and resemble the statistic proposed by Williams (1977) to test for a monotone trend in dose. Hence, using the asymptotic approximations given above, the null distributions for these statistics can be approximated by

and

respectively, where are the isotonized values of {*Z*_{1}, *Z*_{2}, … , *Z _{k}*} with unit weights and are the isotonized values of {

Therefore, in the absence of deaths prior to the end of the experiment, the null distribution of our test statistic *W* can be approximated by the distribution of

As *V* is a function of independent N(0, 1) random variables, its distribution can be simulated by repeatedly generating *k* + 1 independent standard normals. The level *α* critical value for *W* is the 100(1 — *α*)* ^{th}* percentile of the simulated distribution of

More generally, when some animals die early, the components of *W* are functions of the Poly-3 weights, which provide a simple survival adjustment. However, despite possible survival effects, we approximate the distribution of *W* by the same simulated distribution of *V* described above. We demonstrate that the proposed test performs well in the more general case by simulating a variety of realistic data sets with many deaths before *t _{TS}*. The simulation results show that our test operates at (or below) the nominal level in a wide range of situations typically observed in practice.

Following Peddada et al. (2005), data were simulated from a variety of realistic situations commonly encountered in NTP studies, which typically run for two years and end with a terminal sacrifice. We generated two latent random variables for each animal: *T*_{1}, the time to tumor onset, and *T*_{2}, the time to natural death. A simulated animal develops a tumor before death if and only if *T*_{1} < min(*T*_{2}, *t _{TS}*), where min(

We generated data for *p* historical control groups, a current control group, and three current dose groups. The latent times to tumor onset and death, *T*_{1} and *T*_{2}, for animals in all groups were generated from independent Weibull distributions with survival functions of the form: *P*(*T* > *t*) = *exp*(-*ψt*^{γ}). We assumed that all dose groups had the same shape parameters for *T*_{1} and *T*_{2}, say γ_{1} and γ_{2}, which govern the steepness of the tumor incidence and mortality curves, respectively. Any differences among groups were assumed to arise only through the scale parameters. Let the scale parameters for *T*_{1} and *T*_{2} be denoted by *ψ*_{1ci} and *ψ*_{2ci} in the *i*-th group in the current study (*i* = 1, 2, 3, 4) and by *ψ*_{1hm} and *ψ*_{2hm} in the *m*-th historical control group (*m* = 1, … , *p*). We generated *T*_{1} and *T*_{2} values for the various groups according to the following models for the scale parameters:

and

and

where *ψ*_{1} and *ψ*_{2} are baseline values, *ϕ*_{1i} is specific to dose group *i*, *ϕ*_{2} is common to all dose groups, and for *m* = 1, … ,*p*. Thus, all control groups (current and historical) shared a common mortality scale parameter, *ψ*_{2}, but each had a distinct incidence scale parameter. The incidence scale parameters in the historical groups (*ψ*_{1h1}, *ψ*_{1h2}, … , *ψ*_{1hp}) were perturbed from the current control value (*ψ*_{1c1} = *ψ*_{1}) in proportion to *τ*, to induce extra variation. Our primary focus is on the ratio of the tumor incidence rate in dose group *i* relative to the tumor incidence rate in the current control group, which is represented by .

The simulation specified multiple values for some parameters, which led to 540 configurations. We generated data for p = 5 historical control groups. Results are reported for a typical pattern of dose scores: (*d*_{1}, *d*_{2}, *d*_{3}, *d*_{4}) = (0, 0.5, 1.0, 2.0), which we refer to as 2-fold spacings. We also investigated 5-fold dose spacings, but the results are very similar to those obtained for 2-fold spacings (if not even more favorable for our test), and thus they are not shown. As control death rates in NTP studies are well estimated, and our focus is on tumor incidence, very few mortality configurations were examined. The mortality shape parameter was fixed at γ_{2} = 5 and we derived the baseline scale parameter value that gave a typical control survival rate of 70% at 2 years: *ψ*_{2} = 4.48 × 10^{-8}. Two mortality scale multipliers were used, *ϕ*_{2} = 1 and 1.5, which correspond to dose effects on mortality that can be labeled as “none” and “moderate” (i.e. 70% and 45% survival at 2 years in the high-dose group).

In contrast, we varied many factors influencing tumor incidence rates. We investigated three values for the shape of the tumor onset curve, γ_{1} = 1.5, 3, and 6, and five values for the lifetime tumor rate in the current control group, π_{1} = 0.001, 0.01, 0.05, 0.15, and 0.30. For fixed values of π_{1}, γ_{1}, γ_{2}, and *ψ*_{2}, we used equation (1) to solve for *ψ*_{1}, the baseline incidence scale parameter for an “average” control group (i.e. *X _{m}* = 0). We examined three levels of heterogeneity among the historical control groups, where the heterogeneity parameter

Parameter Values Used in the Simulations. The entries in the last 5 columns correspond to the 5 values of the background tumor rate (π_{1}). The entries in the first 3 rows are the values of the baseline incidence scale parameter (*ψ*_{1}) for **...**

Overall, we investigated 540 configurations by taking all combinations of several factors: mortality scale multiplier (2 levels), shape of incidence curve (3 levels), background tumor rate (5 levels), heterogeneity of control groups (3 levels), and incidence ratio pattern (6 levels). Type I error rates were evaluated for the 90 configurations associated with the null hypothesis of equal incidence rates, and powers were estimated for the 450 configurations associated with various alternative hypotheses. The operating characteristics of *W* and *W _{NTP}* were compared in each situation. Though initially it may seem odd to compare a test which uses historical control data with another test which does not, we view this as a comparison of a new method with the current standard method.

For each configuration, we generated 10,000 sets of current study data (i.e. a control group and three dose groups), and for each set of current study data, we generated a set of data from *p* historical control groups. We estimated the Type I error rates for *W* and *W _{NTP}* by the empirical proportions of the 10,000 trials for which

This section summarizes the operating characteristics of the proposed test (*W*) and the NTP test (*W _{NTP}*) as estimated in our simulation study. Both tests maintained the nominal level (see Figure 2). The Type I error rate did not exceed 0.05 in any of the 90 null cases for

Type I Error Rate Comparison for Proposed Test (*W*) Versus NTP Test (*W*_{NTP}). Different symbols identify the various background tumor rates: 0.001 (diamonds), 0.01 (squares), 0.05 (pluses), 0.15 (circles), and 0.30 (triangles). The diagonal reference line **...**

The proposed test was more powerful than the standard test in almost all situations, with *W* having a fairly large advantage relative to *W _{NTP}* in many cases (see Figure 3). For some configurations, the two tests had approximately the same power, as shown by the symbols along the diagonal line. When the rejection rates differed, however,

Power Comparison for Proposed Test (*W*) Versus NTP Test (*W*_{NTP}). Different symbols identify the various background tumor rates: 0.001 (diamonds), 0.01 (squares), 0.05 (pluses), 0.15 (circles), and 0.30 (triangles). The diagonal reference line shows where **...**

The proposed test performed well compared to the standard NTP test in general, but the most obvious improvement of *W* over *W _{NTP}* was when tumors were rare. For example, when the background tumor rate was 0.001 (i.e. a very rare tumor),

This section illustrates the proposed methodology with real data from two NTP studies. The first analysis focuses on a rare tumor, which is the situation that motivated our research, and the second analysis presents a contrasting example involving a common tumor. In one case, our results strengthen an NTP conclusion that was reached despite rather weak statistical evidence. The other case demonstrates how the increased power of our formal procedure for incorporating data from past studies provides an appealing alternative to the NTP’s informal practice of comparing tumor rates in current dose groups with the range of rates from historical control groups.

Benzophenone is an aryl ketone which is produced in large quantities in the U.S., with the potential for widespread occupational and consumer exposures through its use as a fragrance enhancer, flavor additive, photoinitiator, and ultraviolet curing agent (NTP, 2006). It is also used in the manufacture of pharmaceuticals, insecticides, and agricultural chemicals, as well as being an additive in cosmetics, plastics, and adhesives. Benzophenone does not appear to be mutagenic (NTP, 2006, p. 19), although it could potentially be carcinogenic. Short-term animal studies suggested that the liver and the kidneys were the target organs, though toxicity also was observed in the hematopoietic system.

As a consequence of its widespread use, the NTP conducted a two-year study of male and female mice and rats exposed to benzophenone. This example focuses on histiocytic sarcomas in female rats. Groups of size 50 received doses of 0, 312, 625, or 1250 ppm of benzophenone in their food throughout the study. One rat in the 625 ppm group and two rats in the 1250 ppm group developed histiocytic sarcomas. Based only on the current study data, the NTP’s Poly-3 trend test led to a significance value of *P* = 0.074. Though not statistically significant at the usual 0.05 level, the NTP concluded that there was equivocal evidence of carcinogenic activity of benzophenone in female rats for several reasons (NTP, 2006). First, histiocytic sarcoma is a rare neoplasm in female rats and had not been observed in any controls (0/460) in six recent NTP feed studies. In addition, the same neoplasm was positively correlated with the dose of benzophenone in the current study of female mice (*P* = 0.032), and there was a marginally significant trend (*P* = 0.058) observed for another hematopoietic system lesion (mononuclear leukemia) in female rats.

Using the proposed methodology, which formally accounts for the historical control data from the six recent feed studies, we find a significant dose-related trend (*P* = 0.004) in histiocytic sarcoma among female rats. Thus, our method uses historical information to bolster the weak statistical evidence which would otherwise be obtained if considering only the concurrent data. Our results provide formal support for the biologic evidence that fueled the NTP’s suspicion that benzophenone is carcinogenic in female rats.

Gallium arsenide is a by-product of aluminum and zinc extraction (NTP, 2000). Due to its photovoltaic properties, this chemical is used extensively when producing lasers, photodetectors, light-emitting diodes, microwave devices, solar cells, and semicon-ductors. The most common exposure to gallium arsenide occurs when workers inhale small particles during the manufacturing of these devices. As in the case of benzophenone, gallium arsenide does not appear to be mutagenic (NTP, 2000, p. 27), even though it could potentially be carcinogenic. While little is known about the effects of gallium arsenide on humans, short-term rodent studies suggest that the lung is the primary target organ, with toxic effects also seen in the kidney, liver, immune system, and male reproductive system, as well as in fetal development and heme biosynthesis.

As a result of its extensive use in the microelectronics industry, the NTP conducted a two-year inhalation study of male and female mice and rats exposed to gallium arsenide (NTP, 2000). In this example, we focus on malignant lymphomas in female mice. Groups of 50 female mice were exposed in inhalation chambers to doses of 0, 0.1, 0.5, or 1.0 *mg/m*^{3} of gallium arsenide. The corresponding numbers of mice with a malignant lymphoma were 3, 8, 11, and 10, respectively, and the NTP trend test produced a significance value of *P* = 0.035. Even if a statistically significant result is observed in the current study, the NTP often re-evaluates the significance of dose effects on tumor rates in the current study by comparing the current rates with the range of rates observed in control animals from past studies. For instance, in our gallium arsenide example, the survival-adjusted rates of malignant lymphoma in the control and three dose groups are 0.067, 0.175, 0.269, and 0.234, respectively. The NTP compared these rates with the background malignant lymphoma rates from 20 inhalation studies in their historical control database, which ranged from 0.06 to 0.32. As all of the lifetime tumor rates in the current study were within the range of historical rates, the NTP concluded that “the incidences of malignant lymphoma in exposed females were not considered to be exposure related” (NTP, 2000, p. 86), despite a statistically significant result for the current data at the usual 0.05 level of significance. It is easy to verify, however, that methods based on the range of historical tumor rates become less powerful as the number of historical studies increases.

As an alternative to the NTP strategy, we applied our test using 19 of the same 20 historical control groups (data from one study were unavailable). The significance value for our test was *P* = 0.021, which shows that even after incorporating historical control information, the observed dose effects remained statistically significant. Thus, this example suggests that the historical range may not be a good criterion for evaluating the statistical significance of dose effects in the current study.

We also assessed the robustness of our method to the choice of historical data by considering a variety of subsets of 5 historical studies. In each case, the resulting significance value was *P* = 0.02, with differences only in the third decimal place. Furthermore, the inclusion of historical control data from as few as 5 recent studies when analyzing the current data may be su cient, as the large sample approximation seems to work reasonably well even in that situation.

The present NTP approach to evaluating animal carcinogenicity experiments applies formal statistical tests only to concurrent data. Historical control data enter the evaluation only informally – mainly in a comparison of the tumor rates in the current study to the range of background tumor rates among the historical controls. Incorporation of historical data into a formal statistical procedure would represent a much needed tool in evaluating results from cancer bioassays. In fact, the Technical Reports Review Subcommittee of the NTP Board of Scientific Counselors recently recommended that a new method be developed for this important problem (see http://ntp.niehs.nih.gov/files/TRRSMins0905.pdf). In this paper we propose such a procedure, which formally incorporates historical control data, adjusts for survival, makes no lethality assumptions, and avoids parametric models.

We want to re-emphasize that our focus is on age-specific tumor incidence, even though this endpoint generally can not be estimated directly. The proposed test and the standard NTP test are most naturally oriented toward comparisons of lifetime rates, but we evaluate their performance with respect to hypotheses about age-specific incidence rates. Both tests use the Poly-3 adjustment to account for dose-related survival diff erences, and structurally they are expressed in terms of survival-adjusted versions of lifetime tumor rates {π* _{i}*} rather than age-specific tumor incidence rates {λ

As noted in Haseman (1992), extra-binomial variation among historical controls can arise from calendar time drift, inter-laboratory variability, and different types of controls. For example, the variability of tumor rates for vehicle controls in inhalation studies often differs from that of control tumor rates in feed studies. In order to minimize extra variability, the current NTP practice is to use the most recent historical control data and also, as far as possible, to limit the data to studies involving the same route of exposure. We believe that the NTP should continue to base their decisions about carcinogenicity on such a strategy of selecting relevant historical control data, as it is not only scientifically meaningful but will also increase the power of our test considerably. Too much variability in the historical control data can result in *W* having less power than *W _{NTP}* in certain extreme situations.

We believe that the proposed test should be used whenever historical control data are incorporated in the analysis. Specifically, the informal range-based method presently used by the NTP should be replaced by a formal statistical test such as *W*. In most practical situations, *W* is at least as powerful as *W _{NTP}* and often is much more powerful. Even when

This research was supported by the Intramural Research Program of the NIH, National Institute of Environmental Health Sciences. The authors thank Dr. Kenny Crump, Dr. Beth Gladen, Dr. Joseph Haseman, the referees, and the editors for their helpful comments and suggestions. The authors also thank Mr. Kevin McGowan for extracting the NTP data from the database which were analyzed in this paper.

^{*}Shyamal D. Peddada (Corresponding author, peddada/at/niehs.nih.gov), Gregg E. Dinse (dinse/at/niehs.nih.gov), and Grace E. Kissling (kissling/at/niehs.nih.gov) are members of the Biostatistics Branch, National Institute of Environmental Health Sciences, MD A3-03, P.O. Box 12233, Research Triangle Park, NC 27709.

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