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HomeMy WebLinkAbout19940599 Ver 1_Complete File_19950616IMPORTANT ToT--z: I (-- J) _ -- Date Time WHILE YOU WERE OUT of ?runA? 1A411099?17 "D Phone- AREA CODE NUMBER EXTENSION TELEPHONED PLEASE CALL CALLED TO SEE YOU WILL CALL AGAIN WANTS TO SEE YOU URGENT RETURNED YOUR CALL Message /t/ CUYrT/?ma !! ?'1 f? __ Signed N.C. Dept. of Environment, Health, lan\(d?) Natural Resources V?rY State of North Carolina Department of Environment, Health and Natural Resources Division of Environmental Management Ja mes B. Hunt, Jr., G ove mor Jonathan & Howes, Secretary A. Preston Howard, Jr., P.E., Director June 16, 1995 Mr. Larry F. Baldwin Land Management Group, Inc. Post Office Box 2522 Wilmington, NC 28402 Dear Mr. Baldwin: M1.9NA A&14 CD F= F4 FILE COPY Thank you for the opportunity to review and comment on the wetland enhancement- mitigation plans for the Lowes tract in Carteret County (DEM #94599). This project is unique because a wetland will be used to receive and treat stormwater runoff from the roof and concrete aprons. The salient ecological issues are the quality of stormwater runoff, and how the additional quantity and quality of water will affect the vegetation, hydrology and water quality of the wetland. We believe our suggestions for monitoring will address these concerns without an extensive effort. Water Quality Monitoring The quality of water leaving the roof and aprons, and entering and leaving the wetland should be assessed. We recommend that water quality leaving the roof and aprons be assessed during the early stages of selected storms. Water should be analyzed for total phosphorus, total nitrogen, nitrate+nitrite-nitrogen, total Kjeldahl-nitrogen, total phosphorus, soluble phosphorus, temperature, pH, conductivity, copper, zinc, and oil and grease. Sampling should occur during one storm during March-June, and another storm July-September. We believe this protocol will address water quality concerns of water leaving the project and entering the wetland. However, this protocol fails to address whether the wetland is assimilating any pollutants (i.e. is the'wetland performing the functions of a stormwater retention basin). The parameters listed above should be analyzed for water entering and leaving the wetland site during peak, moderate and low flows that are associated with the selected storms. Monitoring should occur for three years. Water quality analyses must be performed at a laboratory certified by the Division of Environmental Management. Wetland Vegetation and Hydrology Monitoring In addition to water quality concerns, monitoring should address how the additional quantity and quality of water affect the wetland. Since wetlands are defined using hydrology, soils and vegetation these components should be assessed or monitored. Soils The soil types of the site should be identified and described in the field. Are the types present at the site the same as those identified in the soil manual for the county? Environmental Sciences Branch 4401 Reedy Creek Road Raleigh, North Carolina 27607 Telephone 919-733-9960 FAX # 733-9959 An Equal Opportunity Affumative Action Employer 5096 recycled/109a post consumer paper Ve2etation The plan submitted states that "data to be recorded should include all vegetative types and quantity sufficient enough to attain a representative percentage of vegetative species present." It is not clear if all species within the 0.1 acre plot will be identified and whether density and cover will be measured. A 0.1 acre plot is an appropriate size to sample trees (dbh > 10 cm [4 in]), but is too large for shrubs and herbs. However, reducing the size to sample herbs and shrubs will most likely position the sample plot too close to the monitoring well used as the center of the 0.1 acre plot. A monitoring well used to locate the center of a permanent plot has a disadvantage of attracting people. This results in disturbing the vegetation near the well. We recommend using three 0.05 acre plots for the 1.5 acre site. (This density of sample plots is consistent with Corps of Engineer guidelines for monitoring bottomland hardwood forest restorations.) Sample plots should be placed in a stratified random manner, depending on the homogeneity of soils and vegetation and desired placement of monitoring wells. All woody stems greater than 10 cm in diameter at breast height (dbh) should be identified, counted and the dbh measured. The two monitoring wells may be used as the centers for two of the plots. Since there are few trees present on the site, the composition of shrubs and herbs also should be determined. However, the areas around the monitoring wells should not be used as a sample site. There are a variety of methods that can be used to determine the composition of shrubs. One acceptable method would be to use belt transects (e.g. 2 x 10 m). All woody stems less than 10 cm dbh and greater that 1 m in height could be identified and a visual estimate of cover provided. The plots could be positioned 10 m along a known compass direction from the monitoring wells. We recognize that a quantitative measure of herbaceous plants is time consuming and species composition changes throughout,the growing season. Therefore, we suggest walking through the site, identifying as many plants as you can, and providing a visual estimate of dominance or cover. Vegetation should be assessed once each year during July or August. Hydrology Biannual sampling is not frequent enough to characterize ground and surface water levels. Therefore we recommend using at least one continuous monitoring well for the first year. After the first year, water levels in at least two wells should be noted during site visits. The stratigraphy of the site where the monitoring wells are installed should be described. We believe our suggestions address the ecological concerns with a minimum of effort and expense. However, since the monitoring plan is not complete we are willing to assist in the development of a final plan. Please call if you have any questions. Sincerely, R. Nom o q