The neighborhood model was designed for the purpose of critiquing the
Goodman model, and is not thought of as a plausible method of
producing ecological inferences in its own right (see pp. 43-44).
The neighborhood model's advantage is that it is in the class of
models that are consistent with the method of bounds for each precinct
and thus cannot be rejected solely from information in the aggregate
data (this class of models is described on p. 191). As such, it can
be seen as a special case of EI. Its disadvantage is its assumption
that
, which is of course appropriate in some
cases and far off in others, but whichever it is it assumes the answer
to the question being asked. A consequence of the neighborhood model
assumption having no error term and supposedly holding exactly is that
its standard errors are always zero, which is unreasonable. If,
somewhat more reasonably, the neighborhood model assumption is
approximately plausible for a particular application, then it
is best to run EI with priors suitably adjusted to reflect this
information. If priors are strong enough and not substantially
contradicted by the likelihood, EI will give similar point estimates
to the neighborhood model, but it will give more reasonable (nonzero)
standard errors and confidence intervals for the precinct-level
quantities.