Conservation Commission Agenda (linked)

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Board/CommissionConservation Commission
Meeting DateApril 25, 2024
Pages8
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Wetland Delineation  •  Wetland Assessment & Permitting  •  Wildlife & Botanical Surveys  •  Fisheries & Aquatics  •  GIS Mapping 
 
 
Davison Environmental, LLC  •  10 Maple Street, Chester, CT 06412  •  860-803-0938  •  www.davisonenvironmental.com 
 
April 23, 2024 
 
Mike Ott 
Summerhill Engineering 
60 Wall Street 
Madison, CT 06443 
 
RE: 
Wetland and Watercourse Delineation Report 
 
Williams School Athletic Complex 
 
 
 
Mr. Ott, 
 
I am a Registered Soil Scientist with 24 years of experience conducting wetland delineation in 
Connecticut. I conducted an inspection of the above-referenced Site on November 13 and 
December 19, 2023, as depicted on the attached Wetland Delineation Sketch Map. The purpose 
of the inspection was to delineate Connecticut jurisdictional wetlands and watercourses. The 
inspection was conducted in accordance with the requirements of the Connecticut Inland 
Wetlands and Watercourses Act (P.A. 155). Inland wetlands include soil types designated as 
poorly drained, very poorly drained, alluvial, and floodplain by the National Cooperative Soils 
Survey as may be amended from time to time, of the National Resources Conservation Service 
(NRCS).  Watercourses means rivers, streams, brooks, waterways, lakes, ponds, marshes, 
swamps, bogs and all other bodies of water, natural or artificial, vernal or intermittent.  Intermittent 
watercourses shall be delineated by a defined permanent channel and bank and the occurrence 
of two or more of the following characteristics: (A) Evidence of scour or deposits of recent alluvium 
or detritus, (B) the presence of standing or flowing water for a duration longer than a particular 
storm incident, and (C) the presence of hydrophytic vegetation.    
 
Soils were examined per the aforementioned regulatory requirements. Along each wetland 
boundary, a hand auger was used to investigate the soil profiles to a minimum depth of 20 inches. 
This was necessary to determine the U.S. Department of Agriculture drainage class (per State 
requirements). Soil profiles were reviewed approximately every 15-30 feet along the boundary, 
typically digging one hole on either side of the defining boundary to confirm the wetland limit. 
 

 
-2- 
A single wetland was delineated. It was demarcated in the field with pink plastic flagging tape 
labeled “Wetland Delineation” and numbered 1-24 and 1X-35X. The wetland is predominately a 
hillside groundwater slope forested wetland. The upper reaches of the wetland transition to shrub 
dominated as the tree canopy decreases. At the very upper end near the athletic field, the wetland 
transitions to small marsh that appears to have been created to manage stormwater, with a riprap 
outlet feeding the lower wetland.   
 
Digitally available soil survey information was obtained from the Natural Resources Conservation 
Service to aid in the classification of the soil types present. Wetland soils consist of the Ridgebury, 
Leicester and Whitman complex. This is an undifferentiated mapping unit consisting of two poorly 
drained (Ridgebury and Leicester) and one very poorly drained (Whitman) soil developed on 
glacial till in depressions and drainageways in uplands and valleys.  Their use interpretations are 
very similar, and they typically are so intermingled on the landscape that separation is not 
practical.  The Ridgebury and Leicester series have a seasonal high water table at or near the 
surface (0-6") from fall through spring.  They differ in that the Leicester soil has a more friable 
compact layer or hardpan, while the Ridgebury soils have a dense to very dense compact layer.  
The Whitman soil has a high water table for much of the year and may frequently be ponded. 
The non-wetland soils were not examined in detail, except as was necessary to determine the 
wetland boundary. Non-wetland soils consist of the Canton and Charlton complex. The Canton 
series consists of very deep, well drained soils formed in a loamy mantle underlain by sandy 
glacial till.  They are on nearly level to very steep glaciated plains, hills, and ridges. Permeability 
is moderately rapid in the solum and rapid in the substratum.  The soils developed in a fine sandy 
loam mantle over acid sandy glacial till of Wisconsin age derived mainly from granite and gneiss 
and some fine-grained sandstone.   
The Charlton series is a very deep, well drained loamy soil formed in friable till.  They are nearly 
level to very steep soils on till plains and hills. Depth to bedrock and the seasonal high water table 
is commonly more than 6 feet.  
If you have any questions regarding these findings, please feel free to contact me. 
 
Respectfully submitted, 
 
Eric Davison 
Wetland Scientist 

 
-3- 
Registered Soil Scientist 
eric@davisonenvironmental.com 
www.davisonenvironmental.com 
 
Attachments: (1) Wetland Delineation Sketch Map 
(2) Wetland Photographs 
 

 
 
WETLAND DELINEATION SKETCH MAP 
____________________________________________________________________________________ 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 

 
 
 
 
 
 
 
 
 

 
-2- 
SITE PHOTOGRAPHS 
____________________________________________________________________________________ 
 
 

 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
Photo 2: View of upper reach of wetland showing areas of concentrated flow. 
Photo 1: View of lower reach of wetland. 

 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
Photo 4: View of uppermost segment of wetland which includes a stormwater basin. 
Photo 3: View of upper reach of wetland as it transitions to shrub dominated.