See also Eisner’s Cove Wetland
On July 23, 2022, I participated in a portion of a Sierra Club walk through woodlands and to the Eisner Cover wetland. I entered the woodland from the small parking lot by Hope Avenue and joined the group as they entered that area and proceeded down to the wetland.
Rhodora and Cinnamon Fern in the Upland Forest
On my way back to Hope Avenue from the wetland, I walked up an informal trail and documented occurrence of two common wetland species – Rhodora and Cinnamon Fern – beginning at about 40 meters from the open wetland and well above the very wet area of a lot of sphagnum moss etc.
The first observation proceeding from the wetlands upwards towards Hope Ave. is iNaturalist 127818807 – Rhodora; altitude approx. 63 m or 3 m above the wetland which lies at approx. 60 meters above mean sea level.
The final observation in the series is iNaturalist 127866748 – Rhodora is at approx. 118 m from the wetland, and almost at the edge of the woodland overlooking Hope Avenue, estimated elevation 67 m, i.e. 7 meters above the wetland. There were a total of 6 individual plants or clumps of Rhodora over this interval, and 4 of Cinnamon Fern.
As I proceeded upward towards Hope Avenue there was increasing abundance of Bracken Fern and Sheep Laurel (Kalmia angustifolia); I documented just a couple of examples of those species on iNaturalist. The leaves of Rhodora and Sheep Laurel are superficially similar, but are quite distinctive in detail; by my assessment, the iNaturalist ID was correct for all specimens. Only one Rhodora plant had developing fruit; this plant was the one highest up on the trail, and the most exposed to sunlight.
Both Rhodora and Cinnamon Fern are considered “Facultative Wetland Species”, i.e. “Usually occur in wetlands, but occasionally in non-wetlands. (Wetland indicator code: FACW)”- GoBotany
Trees, large Shrubs
Most of the spruce in this area appears to be Black Spruce. White Pine is most abundant towards the wetland. Red Maple is common throughout. Large shrubs include Serviceberry, Wild Raisin, Mountain Holly; occasional Witch-hazel & Hobblebush.
Common Ground Vegetation
Bluebead Lily occurs often, generally in pure or nearly pure stands. Bracken Fern is common, likewise Sheep Laurel, especially in gaps. Lowbush Blueberry (2 species) is common. Cucumber Root, Rhodora, Cinnamon Fern, Creeping Snowberry. Some Black Huckleberry. Bunchberry is common close to wetland.
How Old are the Black Spruce?
I estimated the age of a stump of black spruce sawed at about 3ft height as 60-63 years; the stump was 6.6″ (17 cm) in diameter. The largest Black Spruce nearby was 16-17″ estimated dbh, so possibly 100 yrs or more in age. See iNaturalist127909671 for details. There was a lot of selective harvesting of forests in the Halifax area up to about the 1970s or 1980s. I observed many old stumps, some over 2 ft in diameter. The forest is easy to walk through, i.e. well past the early successional “pole” or “stem exclusion” stage. It is an Old Forest.
SP5 Forest Vegetation Type
The forest is this area fits the description for NS Forest Vegetation Type SP5
According to that description, the presence of Cinnamon Fern and Creeping Snowberry (also fairly common at this site) indicate “elevated moisture levels”. Rhodora is not cited as a common species for SP5 but clearly is common at the Mt. Hope site. From the description for SP5:
Concept: This early to late successional Vegetation Type (VT) has a coniferous tree canopy dominated by black spruce and a well-developed woody shrub layer. Black spruce / Lambkill / Bracken usually follows stand-replacing disturbance such as fire, windthrow or harvesting.
Vegetation: Black spruce is the dominant overstory tree with lesser balsam fir. Hybrid (red/black) spruce may also form a significant portion of the canopy. Red maple, white birch, white pine and tamarack are scattered throughout some stands. The shrub layer is dominated by balsam fir and black spruce with lesser red maple. Other characteristic species include wild raisin, lambkill, velvet-leaf blueberry and false holly. Herb and bryophyte diversity is generally low, with bracken the most common herb and smaller amounts of pink lady’s slipper, cow-wheat and teaberry. Schreber’s moss, wavy dicranum and stair-step moss usually dominate the bryophyte layer. The presence of creeping snowberry, cinnamon fern, stair-step moss and patches of sphagnum moss indicate elevated moisture levels.
Successional Dynamics: Nutrient poor soils associated with this VT lead to an edaphic climax community dominated by black spruce. Historically SP5 stands originated from fire disturbance creating mainly even-aged stands. With less frequent disturbance events, white pine may become more prominent in the overstory, possibly leading to a SP4 (White pine / Blueberry / Bracken) community. White pine may also develop a super canopy overtopping an even-aged forest condition of black spruce. SP5 is the successional endpoint for many VTs in the SP group.
Environmental Setting: SP5 is associated with fresh to moist, nutrient poor soils. Thick, ericaceous duff layers are common which limit regeneration by seed unless disturbance creates more exposed micro-sites. Without disturbance, black spruce regeneration is usually by vegetative layering. This VT can be found throughout Nova Scotia on a variety of soils with low nutrient status. This VT is widespread and common across the Maritime Provinces.
A Thick Duff Layer
I dug a hole in the forest floor at one position. There were 2-3 cm of fresh organic matter over thick “duff” down to a boulder at approximately 30 cm depth; the lower 15 cm or so were very wet. See Chojnacky et al., 2009 for a definition of duff, and comments on its importance in carbon storage; 30 cm of duff is a lot.
Conclusions: water and carbon storage
The fairly common occurrence of Cinnamon Fern and of Creeping Snowberry and Rhodora over most of the slope suggest that the forest floor holds a lot of water. There was a thick duff layer, suggesting that the forest floor also holds a lot of carbon, and it was very wet in the lower part of the profile.
Thus it can be expected that clearing of the forest will result in substantial loss of carbon, contributing to global warming; and in much more erratic flows of water into the wetland, likely resulting in excessive flooding at times and severe drought at other times.
At least part of the the wetland is classified as a fen and as such is highly dependent on the integrity of the surrounding, mostly forested uplands. Erratic water flows combined with greatly increased nutrient inputs from an urbanized environment could be sufficient to trigger a change in the wetland from a carbon-storing system, to a carbon-emitting system. potentially even to a “carbon bomb“.
These factors and possibilities have apparently not been considered in approving the area for development.
My observations were limited and informal but surely are sufficient to indicate that a proper Environmental Assessment is required before proceeding with any development of the forested upland in the area of the Eisner Wetland.
– David Patriquin, July 25, 2022
I will refine this description if and as I am able to make more visits to the area.