Distribution of
P. cinereus are in close contact with the soil on the forest floor. As deciduous forests mature, acid deposition can accelerate the acidification of soils. Acidic conditions can limit the distribution of amphibians and the numbers of sibling species, while the pH value of soil has a strong effect on the density and distribution of
P. cinereus. When choosing between acidic and neutral soils,
P. cinereus prefers to occupy more neutral soils.
P. cinereus is rarely found in soils with a pH value of 3.7, and relatively more to be found in soils with a pH value of about 3.8 or higher. Juvenile
P. cinereus have never been found in soils with a pH value lower than 3.7. Similar conclusions have also been supported in the laboratory.
P. cinereus prefers to occupy substrates near neutral pH. A pH value between 2.5 and 3 results in acute mortality, while a pH value between 3 and 4 results in chronic mortality. Low pH will reduce their growth and respiration. Slowed growth and delayed metamorphosis make juvenile
P. cinereus more vulnerable to predators and has serious consequences for population survival. Several other factors, such as moisture and temperature, can affect the population density or dispersion of
Botrytis as well. During prolonged dry periods, individuals move down into the soil, while during short dry periods they retreat under logs or rocks. They will avoid very warm areas, and when the temperature drops to 4–5 Celsius degrees, they will retreat to the ground as well. The optimum temperature is 10 to 15 Celsius degrees. Moreover, intraspecific and
interspecific competition also affected the distribution of
P. cinerea. Individuals confine themselves to moist
microhabitats (beneath rocks, woody debris, etc. as well as beneath the soil) for long periods of time in order to maintain hydration when surface conditions are inhospitably dry or hot, and are only active on the surface to travel, forage, or reproduce for short periods. The duration of surface activity is directly limited by the rate of cutaneous water loss to the environment, which is influenced by environmental variables such as altitude, forest canopy cover, and the amount of recent precipitation. Spatial distributions of the salamander
Plethodon cinereus is observed to be seasonal. In spring,
Plethodon cinereus are more likely to exist in groups of around 2 to 7 individuals under some object covers such as rocks and wood, than in the other seasons, while the density on the forest floor stays constant. This is because that spatial dispute starts in spring. A study in Blackrock Mountain, Virginia indicates that the mean number of salamanders in each quadrant of 100*100 m varies from 1.6 to 3 in spring compared to 0.8 to 1.8 in summer. A significant increase in the spatial distribution of
P. cinereus from spring to summer is thought to be due to intraspecific interference competition. The cover objects on the ground can be a good choice of moisture refuge for
P. cinereus during the rainy season. The failure of
P. cinereus to forage underground causes them to restrict down to areas under and around the cover objects. Aggression and territoriality under resource, food and shelter limitation are the reasons for the observed spacing. Moreover, the two morphologies have different standard metabolic rates, while lead-phase
P. cinereus favor warm habitats or microclimates. So the strong argument is that the geographic distribution of color form is caused by the selection of physiological traits. ==Behavior==