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�acobson Environmental, PLLC www.jacobsonenvironmental.com <br /> Environmental Consultants Wayne.7acobson, P.S.S., W.D.C., P.W.S.,A.F.S. <br /> ------------------------------------------------------------------------------------------------------------ <br /> 5821 Humboldt Avenue North, Brooklyn Center, MN 55430 (612) 802-fi619 Cell <br /> Email: jacobsonenv@msn.com <br /> F12 Iron-Manganese Masses. On flood plains, a layer 4 inches or more thick with 40 percent or <br /> more chroma of 2 or less and 2 percent or more distinct or prominent redox concentrations occurring as <br /> soft iron-manganese masses with diffuse boundaries. The layer occurs entirely within 12 inches of the <br /> soil surface. Iron-manganese masses have value and chroma of 3 or less. Most commonly, they are <br /> black. The thickness requirement is waived if the layer is the mineral surface layer. <br /> User Notes: These iron-manganese masses generally are small (2 to 5mm in size) and have value and <br /> chroma of 3 or less. They can be dominated by manganese and therefore have a color approaching <br /> black. The low matrix chroma must be the result of wetness and not be a weathering or parent material <br /> feature. tron-manganese masses should not be confused with the larger and redder iron nodules <br /> associated with plinthite or with concretions that have sharp boundaries. This indicator occurs on flood <br /> plains along rivers, such as the Apalachicola, Congaree, Mobile, Savannah, and Tennessee Rivers. <br /> Hydroloqv <br /> The presence of current wetland hydrology was determined through direct observation of free water in the <br /> excavated soil pit, saturated soil conditions or soil redoximorphic features. However, the effect of on-or <br /> off-site hydrologic alterations may not always fully be accounted for when routine delineation methods are <br /> used. <br /> In the Midwest Region, hydrology indicators are in four groups: <br /> A) indicators based on the direct observation of surface water or groundwater during a site visit <br /> Indicator A1: SurFace water <br /> Category: Primary <br /> General Description: This indicator consists of the direct, visual observation of survace water(flooding or <br /> ponding)during a site visit. <br /> Indicator A2: High water table <br /> Category: Primary <br /> General Description: This indicator consists of the direct, visual observation of the water table 12 in (30 <br /> cm)or less below the surface in a soil pit, auger hole, or shallow monitoring well. This indicator includes <br /> water tables derived from perched water, throughflow, and discharging groundwater(e.g., in seeps)that <br /> may be moving laterally near the soil surface. <br /> Indicator A3: Saturation <br /> Category: Primary <br /> General Description: Visual observation of saturated soil conditions12 in. (30cm) or less from soil surface <br /> as indicated by water glistening on the surfaces and broken interior faces of soil samples removed from <br /> the pit or auger hole. This indicator must be associated with an existing water table located immediately <br /> below the saturated zone; however, this requirement is waived under episaturated conditions if there is a <br /> restrictive soil layer or bedrock within 12 in. (30 cm) of the surface. <br /> B)indicators of evidence that the site is subject to flooding or ponding <br /> Indicator B1: Water marks <br /> Category: Primary <br /> General Description: water marks are discolorations or stains on the bark of woody vegetation, rocks, <br /> bridge supports, buildings, fences, or other fixed objects as a result of inundation. <br /> Wetland Delineation-Mitigation-Permitting-Monitoring-Banking-Functional Analysis-T&E Surveys g <br /> Phase I Environmental Assessments-EAW's-Soil ID-Soil Analysis& Delineation-Environmental Referrals <br /> Pond &Lake Weed Control & Fish Stocking-Tree Surveys-Natural Resource Management Plans <br />