| Course | PHLT 8500 Advanced Biostatistics |
|---|---|
| Week | Week 8 |
| Paper type | Interaction analysis |
| Length | About 1,020 words, 6 pages |
| Format | APA 7 student paper |
| School | Walden University |
| Program | PhD in Public Health |
| Updated | October 2026 |
Free sample paper for PHLT 8500 Week 8
Does Arsenic Matter More for People With Obesity? An Interaction Analysis of Well Arsenic and Body Mass Index on Diabetes by the Six-Year Visit, Reported on Both the Multiplicative and the Additive Scale
Student Name
Walden University
PHLT 8500: Advanced Biostatistics
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Month Day, Year
Does Arsenic Matter More for People With Obesity? An Interaction Analysis of Well Arsenic and Body Mass Index on Diabetes by the Six-Year Visit, Reported on Both the Multiplicative and the Additive Scale
A Reason to Look
Interaction should be examined when there is a reason to expect it, not searched for across every pair of variables. Here there is a reason. Experimental and population studies suggest that arsenic may impair insulin secretion, while obesity raises insulin resistance, so the two could act together: a person whose insulin demands are already high might be less able to absorb an added insult to secretion. Prospective work has also linked arsenic exposure to incident diabetes (Kuo et al., 2015), so the main association is plausible before any interaction is considered. The question is whether the association between well arsenic and diabetes by the six-year visit differs between participants with and without obesity in the composite private-well cohort, 1,420 adults with 176 new cases. The question was stated in the analysis plan before any stratified result was examined.
Coding for Clarity
To keep the presentation readable, arsenic is split at 10 micrograms per liter, the federal maximum for public water, with wells at or above that value treated as high, and body mass index as 30 or higher versus lower. The continuous versions are analyzed in an appendix with the same conclusions. The model is logistic, adjusted for age, sex, smoking, education and rice intake, with a product term between high arsenic and obesity.
Risks in Four Groups
Knol and VanderWeele (2012) recommend presenting each combination against a single reference group, as here, so readers can see the joint effect alongside each factor's separate effect.
Table 1
Diabetes by the Six-Year Visit by Arsenic and Obesity (Composite Figures)
| Group | Participants | Cases | Risk | Risk ratio vs. reference | |
|---|---|---|---|---|
| Arsenic below 10, BMI under 30 (reference) | 640 | 46 | 7.2% | 1.00 | |
| Arsenic 10 or more, BMI under 30 | 230 | 21 | 9.1% | 1.27 | |
| Arsenic below 10, BMI 30 or more | 400 | 74 | 18.5% | 2.57 | |
| Arsenic 10 or more, BMI 30 or more | 150 | 35 | 23.3% | 3.25 | |
Note. Composite figures, crude risks. Adjusted estimates in Table 2 are similar.
Main Effects, Redefined
Once a product term is in the model, the coefficient for high arsenic no longer describes an average association. It describes the association among participants without obesity, the reference level of the other variable. Likewise, the obesity coefficient describes obesity's association among participants with low-arsenic wells. The product term measures how much the arsenic association, on the log odds scale, differs between the two body mass index groups. Readers who interpret the arsenic coefficient as a general effect after adding an interaction are misreading the model.
Two Scales, Two Answers
On the multiplicative scale, there is essentially no interaction: the odds ratio for high arsenic is about 1.3 in both groups, and their ratio is 1.04. On the additive scale, the picture changes. High arsenic is associated with 1.9 more cases per 100 people among those without obesity but 4.8 more per 100 among those with obesity. The relative excess risk due to interaction, 0.43, summarizes this departure from additivity.
Both answers are correct; they answer different questions. A constant ratio applied to a higher baseline risk produces a larger absolute difference. Because people with obesity start at higher risk, the same relative increase from arsenic adds more cases among them.
Table 2
Interaction on Two Scales (Composite Figures, Adjusted)
| Measure | Estimate | 95% confidence interval | |
|---|---|---|
| Odds ratio for high arsenic, BMI under 30 | 1.31 | 0.77 to 2.23 | |
| Odds ratio for high arsenic, BMI 30 or more | 1.36 | 0.87 to 2.13 | |
| Ratio of odds ratios, multiplicative interaction | 1.04 | 0.52 to 2.08 | |
| Relative excess risk due to interaction, additive interaction | 0.43 | -0.37 to 1.23 | |
| Risk difference for high arsenic, BMI under 30 | 1.9 points | | |
| Risk difference for high arsenic, BMI 30 or more | 4.8 points | | |
Note. Composite figures.
Which Scale Matters for Public Health
For deciding where to act, the additive scale is usually the relevant one. If a county can afford to provide arsenic treatment systems to only some households, the number of cases prevented per household treated is what matters, and that number is larger among residents with obesity. Knol and VanderWeele (2012) recommend reporting both scales for this reason, so readers can judge both the relative strength of association and its absolute consequences.
Precision
The intervals are wide. The relative excess risk interval runs from -0.37 to 1.23, so the data are compatible with no additive interaction as well as with a substantial one. With only 150 participants in the highest-risk group, the analysis is underpowered for interaction, as most interaction analyses are. Detecting an interaction of this size reliably would take several times as many participants with both exposures. The appropriate conclusion is that the absolute burden associated with high arsenic appears larger among people with obesity, consistent with their higher baseline risk, and that the data cannot establish whether the two exposures act together beyond that.
What the Analysis Does Not Show
Even a clear additive interaction would not show biological synergy on its own. An interaction in a model is a pattern in the data, and reading it as a mechanism requires the same causal assumptions as any effect estimate, now for both exposures: no unmeasured confounding of arsenic and no unmeasured confounding of obesity (Greenland et al., 1999). Obesity's confounders, such as physical activity and diet, were never the target of this model's adjustment set, so a causal reading of the joint effect would go beyond what the model was built to support.
Summary
High well arsenic is associated with roughly 30% higher odds of diabetes by the six-year visit regardless of obesity, so there is no multiplicative interaction. Because people with obesity have higher baseline risk, the same relative increase corresponds to more than twice as many additional cases per 100 among them, a departure from additivity whose interval includes zero. Both scales are reported, and the additive scale is the one that informs who should be offered treatment systems first.
References
Greenland, S., Pearl, J., & Robins, J. M. (1999). Causal diagrams for epidemiologic research. Epidemiology, 10(1), 37-48. https://doi.org/10.1097/00001648-199901000-00008
Knol, M. J., & VanderWeele, T. J. (2012). Recommendations for presenting analyses of effect modification and interaction. International Journal of Epidemiology, 41(2), 514-520. https://doi.org/10.1093/ije/dyr218
Kuo, C.-C., Howard, B. V., Umans, J. G., Gribble, M. O., Best, L. G., Francesconi, K. A., Goessler, W., Lee, E., Guallar, E., & Navas-Acien, A. (2015). Arsenic exposure, arsenic metabolism, and incident diabetes in the Strong Heart Study. Diabetes Care, 38(4), 620-627. https://doi.org/10.2337/dc14-1641
PHLT 8500 Week 8 instructions, in plain terms
Interaction assignments ask students to examine whether an exposure's association with the outcome differs across levels of another variable. Faculty expect a prior reason for the interaction, a model with a product term interpreted correctly and results presented in a way that allows readers to see joint and separate effects. Reporting both multiplicative and additive measures, as current guidance recommends, is increasingly required. Students should discuss precision honestly, since interaction analyses are usually underpowered. Expect three or four pages with a four-group table and a table of interaction measures. Coding exposures and modifiers as binary can make the presentation readable, provided continuous versions are checked in an appendix. Many rubrics also ask what the analysis cannot show, such as biological synergy, and whether the modifier's own confounders were addressed.
How this PHLT 8500 Week 8 example is built
A biological rationale for the interaction comes first, supported by cohort findings linking arsenic to incident diabetes. A section explains the binary coding and adjustment set. Table 1 shows participants, cases, risks and risk ratios for four arsenic and obesity groups against one reference, following published recommendations. A section explains how the product term changes the meaning of the main effects. Table 2 gives stratum-specific odds ratios, the ratio of odds ratios, the relative excess risk and risk differences, and the text explains why the scales disagree. Sections address which scale matters, precision and causal limits, then a summary.
Where the marks sit in the PHLT 8500 Week 8 rubric
Graders look for a planned question, correct interpretation and complete presentation. The sample earns these marks by stating the question in advance, explaining that main effects become conditional once a product term enters and following published guidance to report both scales. Showing why a constant ratio yields larger absolute differences at higher baseline risk demonstrates conceptual mastery. Honest treatment of wide intervals shows restraint. Linking the additive scale to decisions about who should receive treatment systems shows public health judgment. Clear tables and correct references round out the grade. Noting that the modifier's confounders were never targeted by the adjustment set shows the author understands the limits of causal claims about joint effects.
Common PHLT 8500 Week 8 mistakes, and how to avoid them
Interaction sections often test a product term, report its p-value and stop. State why you expect interaction before looking. Show all four combinations against one reference. Remember that main effects change meaning once a product term is in the model. Report multiplicative and additive measures, and explain why they can disagree. Connect the additive scale to decisions about allocating resources. Be honest about power. We will prepare an interaction analysis for your own data as a free first sample. Code variables in a way readers can follow, and check continuous versions in an appendix. Say what your interaction can and cannot show about mechanism. Present risk differences alongside ratios, since many readers find additional cases per 100 people easier to interpret than odds ratios.
Get a PHLT 8500 Week 8 example written to your instructions
Send the Week 8 prompt and rubric, the model being extended, and the variable you expect to modify the relationship. An interaction analysis with conditional effects, a predicted-risk figure and the scale question addressed comes back in 24-48h, free when it is your first. The cohort, its product term and every plotted risk are illustrative.
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PHLT 8500 Week 8 questions, answered
Where can I find a free PHLT 8500 Week 8 sample paper?
Read the complete Week 8 analysis on this page, testing whether arsenic's association with diabetes differs by obesity on both multiplicative and additive scales, with real references.
What does a main effect mean when an interaction term is in the model?
It becomes the effect at the reference level of the other variable. In the sample, the arsenic coefficient describes the association among participants without obesity, not an average.
Why can multiplicative and additive interaction disagree?
A constant ratio applied to different baseline risks yields different absolute differences. People with obesity start at higher risk, so the same relative increase from arsenic adds more cases among them.
What is the relative excess risk due to interaction?
It measures departure from additivity: the joint risk ratio minus each separate risk ratio plus one. A positive value means the combined exposures produce more cases than their separate effects would add up to.
Which interaction scale matters for public health?
Usually the additive scale, because it shows where an intervention would prevent the most cases. Guidance recommends reporting both so readers can judge relative strength and absolute impact.