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HomeMy WebLinkAbout20001195 Ver 12_More Info Received_20120305FaR I Solutions ONE COMPANY Transmittal � . Many Solutions Attention Annette M Lucas PE Date 3/1/12 Job No 100062 75476 018 Environmental Engineer To NCDENR I DWQ I Wetlands and Stormwater Branch Phone 919) 807 6375 1650 Mail Service Center Raleigh NC 27699 1650 Regarding CDIA SWMP West Blvd We are sending you ® Attached ❑ Under separate cover via _ the following items ❑ Shop drawings ❑ Prints ® Plans ❑ Samples ❑ Specifications ❑ Copy of Letter ❑ Change Order ® Reports ❑ CDs ❑ Other Copies Date No Descnption 3 3/1/12 1 Updated BMP Operation and Maintenance Plan onginal sign copy 3 3/1/12 2 Bioretention Cell Supplements and Calculations 3 3/1/12 3 New Sheet 14A 14B and 6A of SWMP Colored Plans 3 3/1/12 4 Updated Sheets 1 and 6 of SWMP Colored Plans These are transmitted as checked below ® For approval ❑ Approved as submitted ® For your use ❑ Approved as noted ® As requested ❑ Returned for corrections ❑ For review /comment ❑ Other_ ❑ Forbids due Remarks Enclosed are only the updated documents If enclosures are not as noted please notify us at once C 1pwworkingltpa 1d02274811Transmittal Fom1201201D3 doc HDR Engineering Inc of the Carolinas Employee -owned ® Resubmit 3 copies for approval ❑ Submit _ copies for distnbubon ❑ Return _corrected prints ❑ Prints returned after loan to us 00 MAR 5 2012 OEM WATER QUALITY NDSAW STORMWATER BRANCH Ronald A Geiger PE 128 S Tryon Street Suite 1400 Telephone (704) 338 -6700 Charlotte NC 28202 5004 1 Fax (704) 338 -6760 March 1 2012 Annette M Lucas PE Environmental Engineer NCDENR I DWQ I Wetlands and Stormwater Branch 1650 Mail Service Center Raleigh NC 27699 1650 Re Charlotte Douglas International Airport s (CDIA) UT to Coffey Creek [0308834 11 137 4 C] Dear Ms Lucas On January 9 1212 HDR Engineering Inc of the Carolinas received a letter from the Division of Water Quality (DWQ asking for additional information regarding the CDIA s Modified Storm Water Management Plan (SWMP) specifically the addition of the West Blvd project to the plan We modified the SWMP with bolded text and we are subrrutting only the drawings for West Bl, d that are essential for your review as requested Attached are the relevant document-, which constitute our previous Express Review Stormwater Management Plan submittal package for the above referenced project The following addresses your questions to the letter Bioretention Cell #1 I Does the drainage received by the pipe under Vest Blvd contain runoff from any impervious area? If not it may be better to bypass that runoff and around the cell Bioretention cells work best treating runoff from impervious areas a The pipe does receive water from the impervious area of West Blvd and a future Intermodal facility The plan sheets have been modified to illustrate this The area of treatment only addresses the West Blvd impervious area as required by the permit 2 The plan and supplement show the temporary pool at 711 but it should beat the overflow were at 710 a Plan has been adjusted to comply 3 The supplement states the planting elevation is at 708 75 but the plans show 708 to 709 5 Bioretention cells must be flat throughout their section to function properly a Plan has been adjusted to reflect a flat basin 4 The supplement shows the bottom of the media at 708 58 but it should be the planting elevation minus the 3 of planting media 440 S Church Street Phone 1704) 338 6700 HDR Engineering Inc of the Carolinas Suite 1000 Fax 1704) 338 6760 Charlotte NC 28202 1919 www hdrinc corn NCBELS License No F0116 Ms Annette Lucas March 1 2012 Page 2 of 3 a Plan has been adjusted to comply 5 The supplement shows the depth of sand as an elevation This should be shown as the depth (thickness) of the sand in feet a Plan has been adjusted to comply Bioretention Cell #2 1 On sheet 14B a spot elevation is needed at the overflow to show that it is to be built to elevation 701 (as done on sheet 14A) a Plan has been adjusted to comply 2 The supplement states the planting elevation is at 702 35 but the plans show 702 7 to 703 Bioretention cells must be flat throughout their section to function properly a Plan has been adjusted to reflect a flat basin 3 The depth of sand on the supplement should be shown in feet not inches a Plan has been adjusted to comply 4 The supplement shows the top of the upturned elbow at 700 03 but the plans chow it at 699 7 Please make it consistent a Plan has been adjusted to comply Both Bioretention Cells 1 Please be sure that any changes are consistently reflected or all documents (plans ( ahj rupplement form j O&M forms etc) a Plans and other documents have been updated to be consistent with one another 2 Plans and calculations must be sealed signed and dated by an appropriate NC licensed design pro/essaonat a Plans and calculations are signed and sealed as requested 3 Please venfy the drainage area delineations for the BMPs They do not appear to follow the counters a Plans have been adjusted to include more information as requested with available data 4 The surfaces of the cells are sloped Bioretention cells murt be flat not sloped Please revise a Plan has been adjusted to reflect a flat basin S The plan show pondang over 12 Ponding shall not be greater than 12 Please revue a Plans have been re-, ised to reflect maximum pondang depth HDREngineering Inc ottheCarohnas Ms Annette Lucas March 1 2012 Page 3 of 3 6 An ongznal O&M agreement form must be submitted None were submitted It can be downloaded from http //portal ncdenr � web /wq /su /bmp ch12 a An original O &M agreement is being submitted with this re submittal 7 The SHWT elevation was left blank on the supplements Also a soils report must be provided that states that the SHWT is based on a boring within the footpnnt of each of the proposed cells a Additional information is provided in the re subtruttal to reflect SHWT elevation data received at each BMP location 8 The type of grass sod must be specified Also it should be specified that the sod shall not be fmm a farm grown in taght clay soil that would restrict flow through a Plan has been revised to state sod requirements 9 Both supplements state that a vegetated filter stnp (VFS) isprovided but there are not any Note howeve- that a propery designed VFS per chapter 8 of the BMP Manual is not required for bzoretention cells a The calculations have been revised to reflect the design of the BMP as shown on the plans 70 Please provide supportang calculations for the drawdown and underdrazn sv� ng for each cell a Calculations for the underdrazn sizing and drawdown are included in this re submittal If � ou have anv questions concerning the information in this letter or need additional information please feel free to contact me at (704) 338 6825 Sincerely HDR Engineering, Inc of the Carolinas Ronald A Geiger PE Project Manager cc Jack Christine CDIA Jimmy Jordan CDIA HDR Engineering Inc of the Carolinas AREA WEST O 2 ND PARALLEL RUNWAY REVISED OCTOBER 24, 2008 UPDATED MARCH 1, 2012 PREPARED BY TALIART& MIGHT 4944 Parkway Plaza Boulevard SUITE 350 Charlotte NC 28217 704 426 6070 704 426 6080 (FAX) DR ONE COMPANY I Mang Solutions 440 South Church St Suite 1000 1 Charlotte NC 128202 5004 Phone 704 973 6889 1 Fax 704 338 6760 1 ,�,t1i1969194 .,a ''e►r®e°ea ° ° °3I1 1 OPERATION AND MAINTENANCE AGREEMENT I acknowledge and agree by my signature below that I am responsible for the performance of the six maintenance procedures listed in this OMP I agree to notify DWQ of any problems with the system or prior to any changes to the system or responsible party Print name T J Orr Title Aviation Director Address 5501 Josh Birmingham Pkwv Charlotte, NC 28208 Phone (704) 359 -4000 Signature Date I f�©h e v � A ri � f PS S a Notary Public for the State of North Carolina County of Mecklenburg do hereby certify that T S oa-R- personally appeal before me this Z15� day of NOoew 6evr bland acknowledge the due execubon of the forgoing Operation & Maintenance requirements Witness my hand and iffic alseo SEAL My commission expires 161-65&W2 a J4.. - -aki2 Ar -,2c-ss l L SEAL My commission expires 161-65&W2 a J4.. - -aki2 Ar -,2c-ss Permit No (to be assigned by DWQ) ��� o`'�� WnT �9p� NCDENR ° STORMWATER MANAGEMENT PERMIT APPLICATION FORM 401 CERTIFICATION APPLICATION FORM BIORETENTION CELL SUPPLEMENT This form must be filled out printed and submitted The Required Items Checklist (Part 111) must be printed filled out and submitted along with all of the required information I PROJECT INFORMATION Project name Charlotte Douglas International Airport Contact name Ron Geiger Phone number Date Drainage area number II DESIGN INFORMATION Site Characteristics 704 338 6825 March 2012 Y2 (Bio #1) Drainage area 445 589 0 ft2 Impervious area 34 848 0 ft2 Percent impervious 78% % Design rainfall depth 10 inch Peak Flow Calculations Is pre /post control of the 1 yr 24 hr peak flow required? N (Y or N) 1 yr 24 hr runoff depth in 1 yr 24 hr intensity in /hr Pre development 1 yr 24 hr peak flow ft3 /sec Post development 1 yr 24 hr peak flow ft3 /sec Pre /Post 1 yr 24 hr peak control ft3 /sec Storage Volume Non SA Waters Minimum volume required 4 470 2 ft3 Volume provided 4 500 0 ft3 Storage Volume SA Waters 15 runoff volume ft3 Pre development 1 yr 24 hr runoff ft3 Post development 1 yr 24 hr runoff ft3 Minimum volume required 0 ft3 Volume provided ft3 Form SW401 Bioretention Rev 3 X21 F T (BIO -1- J Part III Page 1 of 3 Y2 (B lo 1) Form SW401 Bioretention Rev 3 Part III Page 2 of 3 Permit No (to be assigned by DWQ) Cell Dimensions Pondmg depth of water 12 inches OK Ponding depth of water 100 ft Surface area of the top of the bioretention cell 4500 0 f{2 OK Length 300 0 ft OK Width 15 0 ft OK -or Radius ft Media and Sods Summary Drawdown time ponded volume 8 hr OK Drawdown time to 24 inches below surface 16 hr OK Drawdown time total 24 hr In situ sod Sod permeability 0 60 in /hr OK Planting media soil Sod permeability 150 in/hr OK Sod composition % Sand (by volume) 85% OK % Fines (by volume) 10% OK % Organic (by volume) 5% OK Total 100% Phosphorus Index (P Index) of media (unitless) Basin Elevations Temporary pool elevation 710 5 fmsl Type of bioretention cell (answer Y to only one of the two following Is this a grassed cell? Y (Y or N) OK Is this a cell with trees /shrubs? N (Y or N) Planting elevation (top of the mulch or grass sod layer) 709 5 fmsl Depth of mulch 017 inches Insufficient mulch depth unless Bottom of the planting media sod 706 33 fmsl Planting media depth 317 ft Depth of washed sand below planting media sod 0 3 ft Are underdrains being installed? Y (Y or N) How many clean out pipes are being installed? 8 OK What factor of safety is used for sizing the underdrams? (See BMP 10 OK Additional distance between the bottom of the planting media and the 1 ft Bottom of the cell required 705 0 fmsl SHWT elevation 696 6 fmsl Distance from bottom to SHWT 8 4 ft OK Y2 (B lo 1) Form SW401 Bioretention Rev 3 Part III Page 2 of 3 Internal Water Storage Zone (IWS) Does the design include IWS Y (Y or N) Elevation of the top of the upturned elbow 706 8 fmsl Separation of IWS and Surface 2 7 ft Planting Plan Number of tree species Number of shrub species Number of herbaceous groundcover species Additional Information Does volume in excess of the design volume bypass the bioretention Y (Y or N) Does volume in excess of the design volume flow evenly distributed Y (Y or N) What is the length of the vegetated filter? ft Does the design use a level spreader to evenly distribute flow? N (Y or N) Is the BMP located at least 30 feet from surface waters (50 feet if SA Y (Y or N) Is the BMP located at least 100 feet from water supply wells? Y (Y or N) Are the vegetated side slopes equal to or less than 31 ? N (Y or N) Is the BMP located in a proposed drainage easement with access to Y (Y or N) Inlet velocity (from treatment system) 1 9 ft/sec Is the area surrounding the cell likely to undergo development in the N (Y or N) Are the slopes draining to the bioretention cell greater than 20 %? N (Y or N) Is the drainage area permanently stabilized? Y (Y or N) Pretreatment Used Gravel and grass Grassed swale Forebay Y Other Permit No (to be assigned by DWQ) OK Ell Show how flow is evenly distributed OK OK Insufficient vegetated side slopes OK Insufficient inlet velocity unless energy OK OK OK NOTES The 10 year design storm flow is evenly distributed through weirs leaving the forbay and entering the bioretention basins and the bypass weir leaving the end forebay The basin has a 40 ft weir leaving the basin An additional weir is located at the end of the forebay for higher storms The side slopes are 21 do to the limited space The inlet velocity from the forbay is entering a bioretention basin that is using grass for its pollutant removal Y-2(-B -io 17 Form SW401 Bioretention Rev 3 Part III Page 3 of 3 dwi- STORMWATER F `N F MANAGEMENT PERMIT APPLICATION FORM 401 CERTIFICATION APPLICATION FORM BIORETENTION CELL SUPPLEMENT This form must be filled out printed and submitted The Required Items Checklist (Part Ill) must be printed filled out and submitted along with all of the required information I PROJECT INFORMATION Project name Charlotte Douglas International Airport Contact name Ron Geiger Phone number 704 338 6825 Date March 2012 Drainage area number L1-4 (Bio #2) II DESIGN INFORMATION Site Characteristics Drainage area 199 543 ff Impervious area 45142 ff Percent impervious 226% % Design rainfall depth 10 inch Peak Flow Calculations Is pre /post control of the 1 yr 24 hr peak flow required? N (Y or N) 1 yr 24 hr runoff depth in 1 yr 24 hr intensity in /hr Pre development 1 yr 24 hr peak flow ft3 /sec Post development 1 yr 24 hr peak flow ft3 /sec Pre /Post 1 yr 24 hr peak control ft3 /sec Storage Volume Non SA Waters Minimum volume required 1 715 9 ft3 Volume provided 1 740 00 ft3 OK Storage Volume SA Waters n/a 15 runoff volume ft3 Pre development 1 yr 24 hr runoff ft3 Post development 1 yr 24 hr runoff ft3 Minimum volume required 0 ft3 Volume provided ft3 1-1 4 (BIO 2) Cell Dimensions Pondmg depth of water 12 inches OK Ponding depth of water 100 ft OK Surface area of the top of the bioretention cell 1740 00 ft OK How many clean out pipes are being installed? Length 58 00 ft OK Width 30 00 ft OK or Radius ft Media and Sods Summary Drawdown time ponded volume 8 hr OK Drawdown time to 24 inches below surface 16 hr OK Drawdown time total 24 hr How many clean out pipes are being installed? In situ soil What factor of safety is used for sizing the underdrains? (See 10 OK Sod permeability 0 60 in /hr OK Planting media sod and the bottom of the cell to account for underdrains Sod permeability 1 50 in /hr OK Sod composition Distance from bottom to SHWT 3 02 ft OK % Sand (by volume) 85% OK % Fines (by volume) 10% OK % Organic (by volume) 5% OK Total 100% Phosphorus Index (P Index) of media (urntless) Basin Elevations Temporary pool elevation 703 50 fmsl Type of bioretention cell (answer Y to only one of the two following questions) Is this a grassed cell? y (Y or N) OK Is this a cell with trees /shrubs? (Y or N) Planting elevation (top of the mulch or grass sod layer) 702 5 fmsl Depth of mulch 017 inches Insufficient mulch depth unless installing grassed cell Bottom of the planting media sod 699 35 fmsl Planting media depth 315 ft Depth of washed sand below planting media soil 0 33 ft Are underdrains being installed? Y (Y or N) How many clean out pipes are being installed? 4 OK What factor of safety is used for sizing the underdrains? (See 10 OK BMP Manual Section 12 3 6) Additional distance between the bottom of the planting media 1 ft and the bottom of the cell to account for underdrains Bottom of the cell required 698 02 fmsl SHWT elevation 695 fmsl Distance from bottom to SHWT 3 02 ft OK 1-1 4 (1310 2) Internal Water Storage Zone (IWS) Does the design include IWS Elevation of the top of the upturned elbow Separation of IWS and Surface Planting Plan Number of tree species Number of shrub species Number of herbaceous groundcover species Additional Information Does volume in excess of the design volume bypass the bioretention cell? Does volume in excess of the design volume flow evenly distributed through a vegetated filter? What is the length of the vegetated filter? Does the design use a level spreader to evenly distribute flow? Is the BMP located at least 30 feet from surface waters (50 feet if SA waters)? Is the BMP localed at least 100 feet from water supply wells? Are the vegetated side slopes equal to or less than 31 Is the BMP located in a proposed drainage easement with access to a public Right of Way (ROW)? Inlet velocity (from treatment system) Is the area surrounding the cell likely to undergo development in the future? Are the slopes draining to the bioretention cell greater than 20 %? Is the drainage area permanently stabilized? Pretreatment Used (Indicate Type Used with an X in the shaded cell) Gravel and grass (811nches gravel followed by 3 5 ft of grass) Grassed swale Forebay Other Y (Y or N) 699 81 fmsl 2 69 ft OK Y (Y or N) OK (Y or N) ft N (Y or N) Show how flow is evenly distributed Y (Y or N) OK Y (Y or N) OK N (Y or N) Insufficient vegetated side slopes Y (Y or N) OK 15 ft/sec Insufficient inlet velocity unless energy dissipating devices are being used N (Y or N) OK N (Y or N) OK Y (Y or N) OK X KI NOTES The 10 year design storm flow is evenly distributed through weirs leaving the forbay and entering the bioretention basins The basin has a 24 ft weir leaving the basin An additional weir is located at the end of the forebay for higher storms The side slopes are 21 do to the steep terrain The inlet velocity from the forbay is entering a biorentention basin that is using grass for its pollutant removal 1-1 4 (BIO 2) CDIA SWMP West Blvd Supplement Bioretention Calculations for CDIA West Blvd HDR Engineering Inc March 2012 Drainage Drainage Pervious Impervious Impervious Section Area Area (ac) Area (sqft) Area (sqft) Area (ac) Y2 (Bio #1) 445 589 102 410 741 34 848 08 L1 4 Bio #2 199 543 46 154 401 45 142 1 0 Total 148 18 Ponding Depth 1 ft Calculated using the Simple Method Design storm rainfall depth 1 in Drainage Area Y2 (Bio #1) Y2 (Bio #1) = Impervious portion of Drainage Area = 008 Total Drainage Area R„= 005 +091A = 012 Volume 3630 *Rp *R,*A = 4 470 cft Width = 15 0 ft Length - 300 ft Dimensions of Bioretention Cell = 4 500 sqft Drainage Area 1-1-4 (Bio #2) L1 4 (Bio #2) = Impervious portion of Drainage Area = 023 Total Drainage Area R„= 005 +091A = 025 Volume 3630 *Rp *R„ *A = 1 716 cft Width = 30 0 ft Length = 58 ft Dimensions of Bioretention Cell = 1 740 sqft K a� CD r CD CA) N w r � < UQ O j G1 O CD W A� U w Cn N O O oo O O O ►- � w p 0 0 O tN W O w O J O � 0 O O N N fD A C �Q n A r A� 0 �s n O D U) CD m CL c co CD 2 v m cn �CD CD w m s 5 N O 05 � 3 N 0 �F O CD r CD p_ P N w r � < UQ O Co w G1 O W U w Cn N O O oo O O fD A C �Q n A r A� 0 �s n O D U) CD m CL c co CD 2 v m cn �CD CD w m s 5 N O 05 � 3 N 0 CDIA SWMP West Blvd Supplement Drainage Area Y2 (Bio #1) Drawdown Calculations Total volume to be treated Permeability of Soil (POS) Surface Area of Soil (SA) Type of rooted plants Target Pollutant Draw down time for ponded area V to be treated PoS * SA of Soil 4470 0 125 4 500 Drawdown Time to 24 in below surface 1 ft of Pondmg Depth into sod is 2 ft of soil is Total Drawdown time Underdrain Sizing for a PVC Q in Volume 4 470 cft Time 24 hr HDR Engineering Inc March 2012 4 470 cft 1 5 in /hr 4 500 cft Grass TSS V _ T Q 0 05 cfs S 0 005 ft/ft Where Q * a1 n 0 011 =1V Sos D 0 07 in D 0 66 in (min) Appling Safety Factor of 10 Using Orifice Equation and a 4 inch pvc CD 04 D 4 in 8 4419E -06 Area 0 09 sqft Havg 1 5 ft g 32 17 ft/s ^2 Q out = Cd * A * SQRT (2gH) _ 7 9 hrs 7 9 hrs 15 9 hrs 23 8 hrs 0 052 cfs 0 34 cfs Using a 4 in underdrain exceeds the flow into the underdrains by 0 29 cfs No backwater will occur CDIA SWMP West Blvd Supplement Drainage Area 1-1 -4 (Bio #2) Drawdown Calculations Total volume to be treated Permeability of Soil (PoS) Surface Area of Sod (SA) Type of rooted plants Target Pollutant Draw down time for ponded area HDR Engineering Inc March 2012 1716 cft 1 5 in /hr 1 740 cft Grass TSS V to be treated PoS * SA of Soil 1716 _ 7 9 hrs 0125 1740 Drawdown Time to 24 in below surface 1 ft of Pondmg Depth into sod is 7 9 hrs 2 ft of sod is 15 8 hrs Total Drawdown time 23 7 hrs Underdrain Sizing Q in Volume 1 716 cft Time 24 hr V = 002 cfs T Q 0 02 cfs 3 S 0 005 ft/ft Where n 0011 'D 1� Sos j D 0 03 in D 0 25 in (min) Appling Safety Factor of 10 Using Orifice Equation and a 4 inch pvc CD 04 D 4 in Area 0 09 sqft Havg 1 5 ft g 32 17 ft/s ^2 Q out = Cd * A * SQRT (2gH) = 0 34 cfs Using a 4 in underdrain exceeds the flow into the underdrains by 0 32 cfs No backwater will occur Groundwater Determination to Support Bioretention Basin Siting 22 February 2012 Introduction In order to obtain groundwater and limited hydrogeological data with respect to proposed bio retention basin siting areas along West Boulevard the Charlotte Douglas International Airport Environmental Affairs Manager Mr Jimmy D Jordan contracted with Probe Technology Inc a licensed North Carolina Well Driller to conduct a limited subsurface investigation at the site(s) of the proposed basins The sites of the proposed basins are shown on those drawings prepared and held by HDR Engineering Charlotte North Carolina Investigation On February 21 2012 Probe Technology a North Carolina Licensed Well Driller Concord NC arrived at the two areas shown on the attached figure and installed a 15 foot piezometer at each location denoted (BR land BR 2) The piezometer probe points were constructed by use of a DT 66 Geo probe track mounted Direct Push vehicle driving 2 75 diameter hollow push point tooling Sod samples were collected continuously at each location from the ground surface to a depth of approximately 15 feet below grade level (BGL) The samples were collected in disposable acetate liners Once procured from the tooling strand the samples were observed and the lithology recorded by Mr Jordan a North Carolina Licensed Geologist The resultant Irthologic descriptions from this work and the locations of the borings are included as Figures 1 and 2 Upon completion of each piezometer the % inch PVC well material was installed into the borehole and constructed as a temporary water level monitoring device A 10 foot long 010' slotted screen section was installed from the bottom of the hole up to an elevation of 5 feet BGL and each well was completed flush to the ground surface by the addition of a 5 foot PVC riser with a compression fitting cap A sand filter pack was placed around the screen section of each piezometer esults The initial observations for the sod profile from BR 1 indicated moisture and damp conditions at approximately 13 feet BGL Approximately 1 hour after installation of the BR 1 a disposable PVC bailer was lowered into the well to check for the presence of water A measurable volume of water was present in the bailer and the depth to water was initially measured by a water level detection device as being approximately 13 4 feet BGL The observations for the sod profile from BR 2 indicated no significant moisture and only slightly moist conditions at approximately 11 feet BGL Approximately 1 hour after installation of the piezometer, a disposable PVC bailer was lowered into the well to check for the presence of water No water was present in the bailer and a static water table surface was not evident when checked with a water level detection device Approximately 24 hours after installation, Mr Jordan returned to the site to check for the presence of groundwater At location BR 1 no groundwater had collected into the piezometer and no measureable amount of water could be collected by the bailer Likewise at location BR 2 no groundwater had collected into the piezometer and no measurable water could be collected into the bailer Conclusions Despite the occurrence of water initially seen at location BR 1 it is the opinion of this investigation that the depth to the shallow water table or surficial aquifer' is greater than 12 feet Within 36 hours prior to the investigation a measurable and prolonged rainfall event had occurred and it is likely that the water initially collected into the well bore was from percolating precipitation through the upper sod column, and not representative of a surfiaal aquifer or static permanent groundwater condition Assuming the piezometer had been installed and screened into the 'static water table then the well would have supplied water as it was being bailed or pumped which it did not Thus this well was dry on the morning of the 22"d AT location BR 2 there was no measurable groundwater penetrated by the installation of the piezometer It is therefore, the professional opinion of the Geologist that the suficial water table at this location is also greater than 12 feet below the surface Limitations The findings conclusions opinions and observations expressed in this report are relative to those activities conducted and those site conditions which existed at the time and date of the investigation and location of the field investigations with respect to the measurements made No warranties are made written or implied with respect to site conditions specifically including geological and hydrogeological conditions that may exist elsewhere in the same geographical locale or that may have existed at different times before or after the investigations were made All measurements expressed in this report should be considered approximate !f G' Jimmy D Jordan,P,� North Carohna`Licented76eologisf 41777 K L sy` f i 22 Feburary 2012 West Blvd. Proposed Bioretention Basin Area Boring Logs Hole # BR-1 Depth Description 0-5 Reddish Brown slightly sandy Clay 5-10 Reddish Brown firm slightly sandy Clay 10-11 Tan, moist sandy Silt or Clay Tan to Deep Brown, M-C sandy Silt w mica, iron, feldspar, Si02 - quite moist, but not 11-15 water bearing. Boring Log Figure 1 Location of Boring UNDERDRAIN PIPE TURN JU-4 Oft #01 ' ' DITCH 'roe O'F PVC- Tor 0" Figure 1 Location of Boring UNDERDRAIN PIPE TURN JU-4 Oft #01 ' ' DITCH 22 Feburary 2012 Hole # BR -2 Depth Description 0 -5 micaceous Reddish Brown fine sandy Silt 5 -7 Same as above 7 -10 Micaceous Brown M sandy Silt; dry 10 -14 Same as above 14 -15 1 Brown to Tan silty F to C Sand as Saprolite with mica, Mn, Iron, etc... moist at 13 ft. Boring Log -porn I GZo hnGi - 3 75, 0 0 IC , Figure 2 Location of Boring Za�V - - - --- +� Ys (eb M _R\ � - Rp. i (SE ERORPIN PIPE TUR (SE N E BECTON 4 -A) i i �I Ys (eb M _R\ � - Rp. i (SE ERORPIN PIPE TUR (SE N E BECTON 4 -A) i