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Appendix 12 · Appendix 12 Traffic Count Results & Drawing LW15-046-02-P-204 For inspection...

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Appendix 12 Traffic Count Results & Drawing LW15-046-02-P-204 For inspection purposes only. Consent of copyright owner required for any other use. EPA Export 22-03-2017:02:09:10
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Page 1: Appendix 12 · Appendix 12 Traffic Count Results & Drawing LW15-046-02-P-204 For inspection purposes only. Consent of copyright owner required for any other use. EPA Export 22-03-2017:02:09:10.

Appendix 12

Traffic Count Results & Drawing LW15-046-02-P-204

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Page 2: Appendix 12 · Appendix 12 Traffic Count Results & Drawing LW15-046-02-P-204 For inspection purposes only. Consent of copyright owner required for any other use. EPA Export 22-03-2017:02:09:10.

ABACUS TRANSPORTATION SURVEYS ABACUS TRANSPORTATION SURVEYS

CAPPAGH ROAD TRAFFIC COUNTS MAY 2016 CAPPAGH ROAD TRAFFIC COUNTS MAY 2016

MANUAL CLASSIFIED JUNCTION TURNING COUNTS ATH/16/048 MANUAL CLASSIFIED JUNCTION TURNING COUNTS ATH/16/048

SITE: 01 DATE: 18th May 2016 SITE: 01 DATE: 18th May 2016

LOCATION: Cappagh Road (Roundabout 1) DAY: Wednesday LOCATION: Cappagh Road (Roundabout 1) DAY: Wednesday

M OVEM EN T 1 M OVEM EN T 2 M OVEM EN T 3 M OVEM EN T 4 M OVEM EN T 5 M OVEM EN T 6

T IM E C A R S LV OGV1 OGV2 B US T OT P C U C A R S LV OGV1 OGV2 B US T OT P C U C A R S LV OGV1 OGV2 B US T OT P C U T IM E C A R S LV OGV1 OGV2 B US T OT P C U C A R S LV OGV1 OGV2 B US T OT P C U C A R S LV OGV1 OGV2 B US T OT P C U

00:00 3 1 0 1 0 5 6 0 0 0 0 0 0 0 0 0 0 0 0 0 0 00:00 0 0 0 0 0 0 0 0 0 0 0 0 0 0 2 0 0 0 0 2 2 8

00:15 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 00:15 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 0 0 1 0 2 3 3

00:30 1 0 0 0 0 1 1 0 0 0 1 0 1 2 0 0 0 0 0 0 0 00:30 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 3

00:45 1 0 0 0 0 1 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 00:45 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1

H / T OT 5 1 0 1 0 7 8 0 0 0 1 0 1 2 0 0 0 0 0 0 0 H / T OT 0 0 0 0 0 0 0 0 0 0 0 0 0 0 3 0 0 1 0 4 5 16

01:00 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 0 1 2 01:00 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 2

01:15 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 01:15 0 0 0 0 0 0 0 0 0 0 0 0 0 0 2 0 0 1 0 3 4 4

01:30 2 0 0 1 0 3 4 0 0 0 0 0 0 0 0 0 0 0 0 0 0 01:30 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 0 0 0 0 1 1 5

01:45 1 0 1 0 0 2 3 0 0 0 0 0 0 0 0 0 0 0 0 0 0 01:45 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 3

H / T OT 3 0 1 1 0 5 7 0 0 0 0 0 0 0 0 0 0 1 0 1 2 H / T OT 0 0 0 0 0 0 0 0 0 0 0 0 0 0 3 0 0 1 0 4 5 14

02:00 1 0 0 0 0 1 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 02:00 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 0 0 3 0 4 8 9

02:15 1 0 0 0 0 1 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 02:15 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1

02:30 0 2 0 1 0 3 4 0 0 0 0 0 0 0 0 0 0 0 0 0 0 02:30 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 0 0 0 0 1 1 5

02:45 0 1 0 0 0 1 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 02:45 0 0 0 0 0 0 0 0 0 0 0 0 0 0 2 0 0 0 0 2 2 3

H / T OT 2 3 0 1 0 6 7 0 0 0 0 0 0 0 0 0 0 0 0 0 0 H / T OT 0 0 0 0 0 0 0 0 0 0 0 0 0 0 4 0 0 3 0 7 11 18

03:00 1 0 2 0 0 3 4 0 0 0 0 0 0 0 0 0 0 0 0 0 0 03:00 0 0 0 0 0 0 0 0 0 0 0 0 0 0 2 1 0 0 0 3 3 7

03:15 2 0 0 0 0 2 2 0 0 0 0 0 0 0 0 0 0 0 0 0 0 03:15 0 0 0 0 0 0 0 0 0 0 0 0 0 0 2 0 0 0 0 2 2 4

03:30 2 1 0 0 0 3 3 0 0 0 0 0 0 0 0 0 0 0 0 0 0 03:30 0 0 0 0 0 0 0 0 0 0 0 0 0 0 3 0 0 0 0 3 3 6

03:45 1 2 0 0 0 3 3 0 0 0 0 0 0 0 0 0 0 0 0 0 0 03:45 0 0 0 0 0 0 0 0 1 0 0 0 1 1 3 0 0 2 0 5 8 12

H / T OT 6 3 2 0 0 11 12 0 0 0 0 0 0 0 0 0 0 0 0 0 0 H / T OT 0 0 0 0 0 0 0 0 1 0 0 0 1 1 10 1 0 2 0 13 16 29

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Page 3: Appendix 12 · Appendix 12 Traffic Count Results & Drawing LW15-046-02-P-204 For inspection purposes only. Consent of copyright owner required for any other use. EPA Export 22-03-2017:02:09:10.

04:00 0 1 0 0 0 1 1 0 0 0 0 0 0 0 0 1 0 0 0 1 1 04:00 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 2 0 0 2 3 5

04:15 1 2 0 0 0 3 3 0 0 0 0 0 0 0 0 0 0 0 0 0 0 04:15 0 0 0 0 0 0 0 0 0 0 0 0 0 0 2 0 1 1 0 4 6 9

04:30 1 0 1 0 0 2 3 0 0 0 0 0 0 0 0 0 0 0 0 0 0 04:30 0 0 0 0 0 0 0 0 0 0 0 0 0 0 3 0 0 0 0 3 3 6

04:45 3 1 0 0 0 4 4 1 0 0 0 0 1 1 1 0 0 0 0 1 1 04:45 0 0 0 0 0 0 0 0 0 0 0 0 0 0 7 0 0 1 0 8 9 15

H / T OT 5 4 1 0 0 10 11 1 0 0 0 0 1 1 1 1 0 0 0 2 2 H / T OT 0 0 0 0 0 0 0 0 0 0 0 0 0 0 12 0 3 2 0 17 21 35

05:00 3 2 1 3 0 9 13 0 0 1 0 0 1 2 0 0 0 1 0 1 2 05:00 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 1 1 1 0 4 6 23

05:15 1 1 3 0 0 5 7 0 0 0 0 0 0 0 0 0 0 0 0 0 0 05:15 0 0 0 0 0 0 0 0 0 0 0 0 0 0 3 0 1 0 0 4 5 11

05:30 7 0 2 0 0 9 10 0 0 0 0 0 0 0 0 0 0 0 0 0 0 05:30 0 0 0 0 0 0 0 0 0 0 0 0 0 0 12 3 1 1 0 17 19 29

05:45 6 2 3 2 0 13 17 0 0 0 0 0 0 0 0 0 0 0 0 0 0 05:45 0 0 0 0 0 0 0 0 0 0 0 0 0 0 9 5 1 0 0 15 16 33

H / T OT 17 5 9 5 0 36 47 0 0 1 0 0 1 2 0 0 0 1 0 1 2 H / T OT 0 0 0 0 0 0 0 0 0 0 0 0 0 0 25 9 4 2 0 40 45 95

06:00 8 2 1 1 0 12 14 0 0 0 0 0 0 0 0 0 0 0 0 0 0 06:00 0 0 0 0 0 0 0 0 0 0 0 0 0 0 2 4 1 2 0 9 12 26

06:15 14 2 4 2 0 22 27 2 0 0 0 0 2 2 0 0 0 0 0 0 0 06:15 1 0 0 0 0 1 1 2 0 0 0 0 2 2 3 1 4 4 0 12 19 51

06:30 25 4 5 3 0 37 43 0 0 0 0 0 0 0 0 1 0 1 0 2 3 06:30 1 0 0 0 0 1 1 0 0 0 0 0 0 0 16 5 2 11 0 34 49 97

06:45 26 3 4 5 0 38 47 0 0 0 0 0 0 0 0 0 0 0 0 0 0 06:45 0 0 0 0 0 0 0 0 0 0 0 0 0 0 16 6 1 11 0 34 49 95

H / T OT 73 11 14 11 0 109 130 2 0 0 0 0 2 2 0 1 0 1 0 2 3 H / T OT 2 0 0 0 0 2 2 2 0 0 0 0 2 2 37 16 8 28 0 89 129 269

07:00 32 6 3 5 0 46 54 2 0 0 0 0 2 2 0 0 0 0 0 0 0 07:00 1 0 0 0 0 1 1 2 0 0 0 0 2 2 13 4 3 6 0 26 35 94

07:15 36 14 5 4 0 59 67 0 0 0 0 0 0 0 0 0 0 0 0 0 0 07:15 0 0 0 0 0 0 0 1 0 0 0 0 1 1 16 8 5 5 0 34 43 111

07:30 62 10 7 4 0 83 92 1 0 0 0 0 1 1 0 0 0 0 0 0 0 07:30 0 0 0 0 0 0 0 1 0 0 0 0 1 1 34 7 8 4 0 53 62 156

07:45 55 7 5 5 0 72 81 7 0 0 0 0 7 7 1 1 0 0 0 2 2 07:45 0 0 0 0 0 0 0 0 0 0 0 0 0 0 55 6 8 3 0 72 80 170

H / T OT 185 37 20 18 0 260 293 10 0 0 0 0 10 10 1 1 0 0 0 2 2 H / T OT 1 0 0 0 0 1 1 4 0 0 0 0 4 4 118 25 24 18 0 185 220 531

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Page 4: Appendix 12 · Appendix 12 Traffic Count Results & Drawing LW15-046-02-P-204 For inspection purposes only. Consent of copyright owner required for any other use. EPA Export 22-03-2017:02:09:10.

ABACUS TRANSPORTATION SURVEYS ABACUS TRANSPORTATION SURVEYS

CAPPAGH ROAD TRAFFIC COUNTS MAY 2016 CAPPAGH ROAD TRAFFIC COUNTS MAY 2016

MANUAL CLASSIFIED JUNCTION TURNING COUNTS ATH/16/048 MANUAL CLASSIFIED JUNCTION TURNING COUNTS ATH/16/048

SITE: 01 DATE: 18th May 2016 SITE: 01 DATE: 18th May 2016

LOCATION: Cappagh Road (Roundabout 1) DAY: Wednesday LOCATION: Cappagh Road (Roundabout 1) DAY: Wednesday

M OVEM EN T 1 M OVEM EN T 2 M OVEM EN T 3 M OVEM EN T 4 M OVEM EN T 5 M OVEM EN T 6

T IM E C A R S LV OGV1 OGV2 B US T OT P C U C A R S LV OGV1 OGV2 B US T OT P C U C A R S LV OGV1 OGV2 B US T OT P C U T IM E C A R S LV OGV1 OGV2 B US T OT P C U C A R S LV OGV1 OGV2 B US T OT P C U C A R S LV OGV1 OGV2 B US T OT P C U

08:00 43 8 2 1 0 54 56 9 0 0 0 0 9 9 0 0 0 0 0 0 0 08:00 0 0 0 0 0 0 0 0 1 0 0 0 1 1 34 5 9 6 0 54 66 133

08:15 54 8 3 8 0 73 85 11 0 0 0 0 11 11 0 1 0 0 0 1 1 08:15 0 0 0 0 0 0 0 4 0 0 0 0 4 4 44 12 2 2 0 60 64 165

08:30 49 7 3 6 0 65 74 11 0 0 0 0 11 11 0 0 1 0 0 1 2 08:30 0 0 0 0 0 0 0 3 0 0 0 0 3 3 38 8 2 2 0 50 54 143

08:45 70 12 3 6 0 91 100 12 0 0 0 0 12 12 0 0 0 0 0 0 0 08:45 0 0 0 0 0 0 0 4 0 0 0 0 4 4 41 8 8 3 0 60 68 184

H / T OT 216 35 11 21 0 283 316 43 0 0 0 0 43 43 0 1 1 0 0 2 3 H / T OT 0 0 0 0 0 0 0 11 1 0 0 0 12 12 157 33 21 13 0 224 251 625

09:00 46 17 5 9 0 77 91 13 0 0 0 0 13 13 2 0 0 0 0 2 2 09:00 0 0 0 0 0 0 0 5 0 0 0 0 5 5 44 11 6 5 3 69 82 193

09:15 23 6 2 3 0 34 39 2 0 0 0 0 2 2 1 0 0 0 0 1 1 09:15 0 0 0 0 0 0 0 3 0 0 0 0 3 3 25 13 7 6 1 52 64 109

09:30 35 11 5 5 0 56 65 5 0 1 0 0 6 7 0 0 0 0 0 0 0 09:30 1 0 0 0 0 1 1 1 0 0 1 0 2 3 22 3 4 3 1 33 40 116

09:45 28 9 3 7 0 47 58 2 0 0 0 0 2 2 3 0 0 2 0 5 8 09:45 0 0 0 1 0 1 2 2 0 1 2 0 5 8 24 5 4 3 2 38 46 124

H / T OT 132 43 15 24 0 214 253 22 0 1 0 0 23 24 6 0 0 2 0 8 11 H / T OT 1 0 0 1 0 2 3 11 0 1 3 0 15 19 115 32 21 17 7 192 232 541

10:00 26 14 7 6 0 53 64 1 1 1 0 0 3 4 1 0 1 0 0 2 3 10:00 0 1 0 1 0 2 3 0 0 0 0 0 0 0 20 9 5 8 0 42 55 129

10:15 17 10 4 4 0 35 42 2 0 0 0 0 2 2 1 0 1 0 0 2 3 10:15 0 0 0 0 0 0 0 1 0 0 0 0 1 1 21 9 8 7 0 45 58 106

10:30 23 15 6 7 0 51 63 0 0 0 0 0 0 0 1 2 0 0 0 3 3 10:30 0 0 1 0 0 1 2 1 1 0 0 0 2 2 28 9 4 6 0 47 57 126

10:45 19 8 3 7 0 37 48 1 2 0 0 0 3 3 0 0 0 0 0 0 0 10:45 0 0 0 0 0 0 0 0 0 0 0 0 0 0 24 12 5 4 0 45 53 103

H / T OT 85 47 20 24 0 176 217 4 3 1 0 0 8 9 3 2 2 0 0 7 8 H / T OT 0 1 1 1 0 3 5 2 1 0 0 0 3 3 93 39 22 25 0 179 223 464

11:00 26 11 5 5 0 47 56 0 0 0 0 0 0 0 2 1 0 0 0 3 3 11:00 0 0 0 0 0 0 0 0 0 0 0 0 0 0 28 3 2 4 2 39 47 106

11:15 18 13 6 7 0 44 56 0 0 0 0 0 0 0 0 0 0 0 0 0 0 11:15 0 0 0 0 0 0 0 0 0 1 0 0 1 2 21 13 3 5 0 42 50 108

11:30 19 13 3 6 0 41 50 1 0 1 1 0 3 5 0 0 0 1 0 1 2 11:30 0 0 0 0 0 0 0 0 0 0 1 0 1 2 23 14 5 5 1 48 58 118

11:45 20 7 6 9 0 42 57 0 0 1 0 0 1 2 4 1 1 0 0 6 7 11:45 0 0 0 0 0 0 0 1 0 0 1 0 2 3 19 13 4 5 0 41 50 118

H / T OT 83 44 20 27 0 174 219 1 0 2 1 0 4 6 6 2 1 1 0 10 12 H / T OT 0 0 0 0 0 0 0 1 0 1 2 0 4 7 91 43 14 19 3 170 205 449

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Page 5: Appendix 12 · Appendix 12 Traffic Count Results & Drawing LW15-046-02-P-204 For inspection purposes only. Consent of copyright owner required for any other use. EPA Export 22-03-2017:02:09:10.

12:00 18 15 12 1 0 46 53 2 0 0 0 0 2 2 3 0 0 0 0 3 3 12:00 0 0 0 0 0 0 0 0 0 0 0 0 0 0 25 8 7 9 0 49 64 123

12:15 23 14 4 9 0 50 64 1 0 0 0 0 1 1 0 0 0 0 0 0 0 12:15 0 0 0 1 0 1 2 1 0 0 0 0 1 1 28 9 6 7 0 50 62 130

12:30 25 8 3 10 0 46 61 0 0 0 0 0 0 0 2 0 0 0 0 2 2 12:30 2 0 0 0 0 2 2 0 0 0 0 0 0 0 29 7 1 6 0 43 51 116

12:45 29 7 5 9 0 50 64 3 0 0 0 0 3 3 3 0 0 1 0 4 5 12:45 0 0 0 0 0 0 0 0 0 0 0 0 0 0 24 4 10 4 0 42 52 125

H / T OT 95 44 24 29 0 192 242 6 0 0 0 0 6 6 8 0 0 1 0 9 10 H / T OT 2 0 0 1 0 3 4 1 0 0 0 0 1 1 106 28 24 26 0 184 230 493

13:00 32 10 2 8 0 52 63 1 0 1 1 0 3 5 1 0 0 0 0 1 1 13:00 0 0 0 0 0 0 0 0 0 1 0 0 1 2 28 8 7 6 1 50 62 133

13:15 15 12 3 6 1 37 47 2 1 0 0 0 3 3 1 0 0 2 0 3 6 13:15 0 0 0 0 0 0 0 0 0 0 0 0 0 0 22 10 2 6 0 40 49 105

13:30 16 6 3 10 0 35 50 2 0 0 0 0 2 2 0 0 0 0 0 0 0 13:30 0 0 0 0 0 0 0 0 0 0 0 0 0 0 17 8 4 8 0 37 49 101

13:45 28 6 4 7 0 45 56 0 0 0 0 0 0 0 0 0 0 0 0 0 0 13:45 0 0 0 0 0 0 0 0 0 0 0 0 0 0 34 9 3 8 0 54 66 122

H / T OT 91 34 12 31 1 169 216 5 1 1 1 0 8 10 2 0 0 2 0 4 7 H / T OT 0 0 0 0 0 0 0 0 0 1 0 0 1 2 101 35 16 28 1 181 226 461

14:00 31 6 3 8 0 48 60 0 0 0 1 0 1 2 1 0 0 0 0 1 1 14:00 0 0 0 1 0 1 2 1 1 0 1 0 3 4 27 10 8 9 0 54 70 140

14:15 23 12 5 7 1 48 61 0 0 0 0 0 0 0 0 1 0 0 0 1 1 14:15 0 0 0 0 0 0 0 0 0 0 0 0 0 0 25 4 6 3 0 38 45 107

14:30 18 12 7 3 0 40 47 2 0 0 1 0 3 4 1 1 1 0 0 3 4 14:30 0 0 0 1 0 1 2 0 0 0 0 0 0 0 29 12 5 11 0 57 74 131

14:45 21 5 7 6 0 39 50 1 0 0 0 0 1 1 0 0 0 0 0 0 0 14:45 1 0 0 0 0 1 1 0 0 0 0 0 0 0 25 9 5 4 1 44 53 105

H / T OT 93 35 22 24 1 175 218 3 0 0 2 0 5 8 2 2 1 0 0 5 6 H / T OT 1 0 0 2 0 3 6 1 1 0 1 0 3 4 106 35 24 27 1 193 241 482

15:00 17 8 8 6 0 39 51 0 0 0 0 0 0 0 1 0 1 0 0 2 3 15:00 1 0 0 0 0 1 1 0 0 0 0 0 0 0 33 10 9 5 0 57 68 122

15:15 17 9 4 6 0 36 46 0 1 0 0 0 1 1 1 0 0 0 0 1 1 15:15 1 0 0 0 0 1 1 0 0 0 0 0 0 0 27 6 5 8 0 46 59 108

15:30 18 10 10 10 1 49 68 0 1 0 0 0 1 1 2 0 0 0 0 2 2 15:30 0 0 0 0 0 0 0 0 0 0 0 0 0 0 24 13 4 6 0 47 57 128

15:45 16 8 1 12 0 37 53 1 0 0 0 0 1 1 6 0 0 0 0 6 6 15:45 0 0 0 0 0 0 0 0 0 0 0 0 0 0 38 7 5 11 0 61 78 138

H / T OT 68 35 23 34 1 161 218 1 2 0 0 0 3 3 10 0 1 0 0 11 12 H / T OT 2 0 0 0 0 2 2 0 0 0 0 0 0 0 122 36 23 30 0 211 262 496

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Page 6: Appendix 12 · Appendix 12 Traffic Count Results & Drawing LW15-046-02-P-204 For inspection purposes only. Consent of copyright owner required for any other use. EPA Export 22-03-2017:02:09:10.

ABACUS TRANSPORTATION SURVEYS ABACUS TRANSPORTATION SURVEYS

CAPPAGH ROAD TRAFFIC COUNTS MAY 2016 CAPPAGH ROAD TRAFFIC COUNTS MAY 2016

MANUAL CLASSIFIED JUNCTION TURNING COUNTS ATH/16/048 MANUAL CLASSIFIED JUNCTION TURNING COUNTS ATH/16/048

SITE: 01 DATE: 18th May 2016 SITE: 01 DATE: 18th May 2016

LOCATION: Cappagh Road (Roundabout 1) DAY: Wednesday LOCATION: Cappagh Road (Roundabout 1) DAY: Wednesday

M OVEM EN T 1 M OVEM EN T 2 M OVEM EN T 3 M OVEM EN T 4 M OVEM EN T 5 M OVEM EN T 6

T IM E C A R S LV OGV1 OGV2 B US T OT P C U C A R S LV OGV1 OGV2 B US T OT P C U C A R S LV OGV1 OGV2 B US T OT P C U T IM E C A R S LV OGV1 OGV2 B US T OT P C U C A R S LV OGV1 OGV2 B US T OT P C U C A R S LV OGV1 OGV2 B US T OT P C U

16:00 22 9 0 9 1 41 54 0 1 0 0 0 1 1 3 0 0 0 0 3 3 16:00 3 0 0 0 0 3 3 0 0 0 0 0 0 0 48 9 3 10 0 70 85 145

16:15 25 7 3 7 0 42 53 0 0 0 0 0 0 0 4 1 0 0 0 5 5 16:15 3 0 0 0 0 3 3 0 0 0 0 0 0 0 36 11 4 3 0 54 60 121

16:30 36 9 3 9 1 58 72 1 2 1 0 0 4 5 4 1 1 0 0 6 7 16:30 1 0 0 0 0 1 1 0 0 0 0 0 0 0 47 16 1 1 0 65 67 151

16:45 35 13 3 6 0 57 66 2 1 0 0 0 3 3 7 0 0 0 0 7 7 16:45 2 0 0 0 0 2 2 0 0 0 0 0 0 0 60 4 2 5 0 71 79 157

H / T OT 118 38 9 31 2 198 245 3 4 1 0 0 8 9 18 2 1 0 0 21 22 H / T OT 9 0 0 0 0 9 9 0 0 0 0 0 0 0 191 40 10 19 0 260 290 574

17:00 68 11 2 4 0 85 91 1 0 0 0 0 1 1 11 0 0 0 0 11 11 17:00 4 0 0 0 0 4 4 0 0 0 0 0 0 0 78 10 6 4 0 98 106 213

17:15 54 7 5 4 0 70 78 0 0 0 0 0 0 0 5 0 0 0 0 5 5 17:15 5 0 0 0 0 5 5 0 0 0 0 0 0 0 73 9 2 4 0 88 94 182

17:30 70 7 5 3 0 85 91 1 0 0 0 0 1 1 7 0 0 0 0 7 7 17:30 0 0 0 0 0 0 0 0 0 0 0 0 0 0 84 7 3 3 0 97 102 202

17:45 40 3 3 3 0 49 54 0 0 0 1 0 1 2 7 0 0 1 0 8 9 17:45 2 0 0 0 0 2 2 0 0 0 0 0 0 0 40 8 1 0 0 49 50 118

H / T OT 232 28 15 14 0 289 315 2 0 0 1 0 3 4 30 0 0 1 0 31 32 H / T OT 11 0 0 0 0 11 11 0 0 0 0 0 0 0 275 34 12 11 0 332 352 715

18:00 26 5 0 0 0 31 31 0 0 0 0 0 0 0 4 0 0 0 0 4 4 18:00 2 0 0 0 0 2 2 0 0 0 0 0 0 0 60 10 1 4 0 75 81 118

18:15 27 3 3 1 0 34 37 0 0 0 0 0 0 0 3 0 0 0 0 3 3 18:15 0 0 0 0 0 0 0 0 0 0 0 0 0 0 44 4 1 1 0 50 52 92

18:30 13 2 0 1 0 16 17 0 0 0 0 0 0 0 1 0 0 0 0 1 1 18:30 0 0 0 0 0 0 0 0 0 0 0 0 0 0 28 4 2 1 0 35 37 56

18:45 22 3 2 3 0 30 35 0 0 0 0 0 0 0 2 0 0 0 0 2 2 18:45 1 0 0 0 0 1 1 0 0 0 0 0 0 0 34 3 1 1 0 39 41 79

H / T OT 88 13 5 5 0 111 120 0 0 0 0 0 0 0 10 0 0 0 0 10 10 H / T OT 3 0 0 0 0 3 3 0 0 0 0 0 0 0 166 21 5 7 0 199 211 344

19:00 16 2 0 1 0 19 20 0 0 0 0 0 0 0 1 0 0 0 0 1 1 19:00 0 0 0 0 0 0 0 0 0 0 0 0 0 0 27 7 1 0 0 35 36 57

19:15 6 1 3 0 0 10 12 0 0 0 1 0 1 2 1 0 0 0 0 1 1 19:15 0 0 0 0 0 0 0 0 0 0 0 0 0 0 23 2 3 1 1 30 34 49

19:30 9 1 0 0 0 10 10 1 0 0 0 0 1 1 0 0 0 1 0 1 2 19:30 1 0 0 0 0 1 1 0 0 0 0 0 0 0 20 2 1 1 0 24 26 40

19:45 10 0 1 0 0 11 12 0 0 0 0 0 0 0 1 0 0 0 0 1 1 19:45 1 0 0 0 0 1 1 0 0 0 0 0 0 0 6 1 1 0 0 8 9 22

H / T OT 41 4 4 1 0 50 53 1 0 0 1 0 2 3 3 0 0 1 0 4 5 H / T OT 2 0 0 0 0 2 2 0 0 0 0 0 0 0 76 12 6 2 1 97 104 168

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Page 7: Appendix 12 · Appendix 12 Traffic Count Results & Drawing LW15-046-02-P-204 For inspection purposes only. Consent of copyright owner required for any other use. EPA Export 22-03-2017:02:09:10.

20:00 9 2 0 0 0 11 11 0 0 0 0 0 0 0 1 0 0 0 0 1 1 20:00 1 0 0 0 0 1 1 0 0 0 0 0 0 0 16 2 2 0 2 22 25 38

20:15 4 0 0 0 0 4 4 0 0 0 0 0 0 0 1 0 0 0 0 1 1 20:15 0 0 0 0 0 0 0 1 0 0 0 0 1 1 9 1 0 0 0 10 10 16

20:30 5 0 0 1 0 6 7 0 0 0 1 0 1 2 2 0 0 0 0 2 2 20:30 0 0 0 0 0 0 0 1 0 0 0 0 1 1 8 0 0 1 0 9 10 23

20:45 7 1 1 0 0 9 10 0 0 0 0 0 0 0 0 0 0 1 0 1 2 20:45 0 0 0 0 0 0 0 1 0 0 0 0 1 1 15 1 1 0 0 17 18 30

H / T OT 25 3 1 1 0 30 32 0 0 0 1 0 1 2 4 0 0 1 0 5 6 H / T OT 1 0 0 0 0 1 1 3 0 0 0 0 3 3 48 4 3 1 2 58 63 107

21:00 5 2 0 0 0 7 7 0 0 0 0 0 0 0 0 0 0 0 0 0 0 21:00 1 0 0 0 0 1 1 0 0 0 0 0 0 0 14 0 0 0 0 14 14 22

21:15 3 4 0 0 0 7 7 0 0 0 0 0 0 0 0 0 0 0 0 0 0 21:15 0 0 0 0 0 0 0 0 0 0 1 0 1 2 6 1 0 0 0 7 7 16

21:30 3 0 1 1 0 5 7 0 0 0 0 0 0 0 0 0 0 0 0 0 0 21:30 0 0 0 0 0 0 0 0 0 0 0 0 0 0 9 3 0 1 0 13 14 21

21:45 2 1 0 0 0 3 3 0 0 0 0 0 0 0 0 0 0 0 0 0 0 21:45 0 0 0 0 0 0 0 0 0 0 0 0 0 0 7 2 0 1 0 10 11 14

H / T OT 13 7 1 1 0 22 24 0 0 0 0 0 0 0 0 0 0 0 0 0 0 H / T OT 1 0 0 0 0 1 1 0 0 0 1 0 1 2 36 6 0 2 0 44 47 74

22:00 3 0 0 0 0 3 3 0 0 0 0 0 0 0 0 0 0 0 0 0 0 22:00 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 0 0 0 0 1 1 4

22:15 0 0 0 1 0 1 2 0 0 0 0 0 0 0 0 0 0 0 0 0 0 22:15 0 0 0 0 0 0 0 0 0 0 0 0 0 0 2 1 0 0 0 3 3 5

22:30 2 1 0 0 0 3 3 0 0 0 0 0 0 0 0 0 0 0 0 0 0 22:30 0 0 0 0 0 0 0 0 0 0 0 0 0 0 2 1 0 0 0 3 3 6

22:45 5 0 0 1 0 6 7 0 0 0 0 0 0 0 0 0 0 0 0 0 0 22:45 0 0 0 0 0 0 0 0 0 0 0 0 0 0 3 0 1 0 0 4 5 12

H / T OT 10 1 0 2 0 13 16 0 0 0 0 0 0 0 0 0 0 0 0 0 0 H / T OT 0 0 0 0 0 0 0 0 0 0 0 0 0 0 8 2 1 0 0 11 12 27

23:00 1 0 0 0 0 1 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 23:00 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 0 0 0 0 1 1 2

23:15 2 0 0 0 0 2 2 0 0 0 0 0 0 0 0 0 0 0 0 0 0 23:15 1 0 0 0 0 1 1 2 0 0 0 0 2 2 4 0 0 0 0 4 4 9

23:30 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 23:30 1 0 0 0 0 1 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1

23:45 5 1 0 0 0 6 6 0 0 0 0 0 0 0 0 0 0 0 0 0 0 23:45 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 6

H / T OT 8 1 0 0 0 9 9 0 0 0 0 0 0 0 0 0 0 0 0 0 0 H / T OT 2 0 0 0 0 2 2 2 0 0 0 0 2 2 5 0 0 0 0 5 5 180 0 :0 0 -

0 0 :0 01694 476 229 306 5 2710 3227 104 10 7 8 0 129 143 104 12 7 12 0 135 154

0 0 :0 0 -

0 0 :0 038 1 1 5 0 45 52 38 4 3 7 0 52 63 1908 451 241 284 15 2899 3404 7043

0 6 :0 0 -

2 2 :0 01638 458 216 296 5 2613 3111 103 10 6 7 0 126 138 103 11 7 10 0 131 148

0 6 :0 0 -

2 2 :0 036 1 1 5 0 43 50 36 3 3 7 0 49 60 1838 439 233 273 15 2798 3284 6790

0 7:0 0 -

19 :0 01486 433 196 282 5 2402 2872 100 10 6 5 0 121 131 96 10 7 7 0 120 133

0 7:0 0 -

19 :0 030 1 1 5 0 37 44 31 3 3 6 0 43 52 1641 401 216 240 12 2510 2942 6173

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Page 8: Appendix 12 · Appendix 12 Traffic Count Results & Drawing LW15-046-02-P-204 For inspection purposes only. Consent of copyright owner required for any other use. EPA Export 22-03-2017:02:09:10.

ABACUS TRANSPORTATION SURVEYS ABACUS TRANSPORTATION SURVEYS

CAPPAGH ROAD TRAFFIC COUNTS MAY 2016 CAPPAGH ROAD TRAFFIC COUNTS MAY 2016

MANUAL CLASSIFIED JUNCTION TURNING COUNTS ATH/16/048 MANUAL CLASSIFIED JUNCTION TURNING COUNTS ATH/16/048

SITE: 02 DATE: 18th May 2016 SITE: 02 DATE: 18th May 2016

LOCATION: Cappagh Road (Roundabout 2) DAY: Wednesday LOCATION: Cappagh Road (Roundabout 2) DAY: Wednesday

M OVEM EN T 1 M OVEM EN T 2 M OVEM EN T 3 M OVEM EN T 4 M OVEM EN T 5 M OVEM EN T 6

T IM E C A R S LV OGV1 OGV2 B US T OT P C U C A R S LV OGV1 OGV2 B US T OT P C U C A R S LV OGV1 OGV2 B US T OT P C U T IM E C A R S LV OGV1 OGV2 B US T OT P C U C A R S LV OGV1 OGV2 B US T OT P C U C A R S LV OGV1 OGV2 B US T OT P C U

00:00 1 0 0 0 0 1 1 3 0 0 0 0 3 3 2 0 0 0 0 2 2 00:00 0 0 0 0 0 0 0 0 1 0 1 0 2 3 2 0 0 0 0 2 2 11

00:15 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 0 0 1 0 2 3 00:15 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 3

00:30 0 0 0 0 0 0 0 1 0 0 1 0 2 3 0 0 0 0 0 0 0 00:30 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 3

00:45 0 0 0 0 0 0 0 1 0 0 0 0 1 1 0 0 0 0 0 0 0 00:45 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1

H / T OT 1 0 0 0 0 1 1 5 0 0 1 0 6 7 3 0 0 1 0 4 5 H / T OT 0 0 0 0 0 0 0 0 1 0 1 0 2 3 2 0 0 0 0 2 2 19

01:00 0 0 1 0 0 1 2 0 0 0 0 0 0 0 0 0 0 1 0 1 2 01:00 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 0 0 0 1 1 5

01:15 0 0 0 0 0 0 0 0 0 0 0 0 0 0 2 0 0 0 0 2 2 01:15 0 0 0 1 0 1 2 0 0 0 0 0 0 0 0 1 0 0 0 1 1 5

01:30 1 0 0 0 0 1 1 1 0 0 1 0 2 3 1 0 0 0 0 1 1 01:30 0 0 0 0 0 0 0 1 0 0 0 0 1 1 3 0 0 0 0 3 3 9

01:45 1 1 0 0 0 2 2 1 0 1 0 0 2 3 0 0 0 0 0 0 0 01:45 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 0 0 0 1 1 6

H / T OT 2 1 1 0 0 4 5 2 0 1 1 0 4 6 3 0 0 1 0 4 5 H / T OT 0 0 0 1 0 1 2 1 0 0 0 0 1 1 3 3 0 0 0 6 6 25

02:00 0 0 0 0 0 0 0 1 0 0 0 0 1 1 0 0 0 3 0 3 7 02:00 1 0 0 0 0 1 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 9

02:15 1 1 0 0 0 2 2 1 0 0 0 0 1 1 0 0 0 0 0 0 0 02:15 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 3

02:30 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 0 0 0 0 1 1 02:30 0 0 0 0 0 0 0 0 2 0 1 0 3 4 0 0 0 0 0 0 0 5

02:45 1 0 0 1 0 2 3 0 0 0 0 0 0 0 2 0 0 0 0 2 2 02:45 0 0 0 0 0 0 0 0 1 0 0 0 1 1 0 0 0 0 0 0 0 6

H / T OT 2 1 0 1 0 4 5 2 0 0 0 0 2 2 3 0 0 3 0 6 10 H / T OT 1 0 0 0 0 1 1 0 3 0 1 0 4 5 0 0 0 0 0 0 0 24

03:00 2 0 0 0 0 2 2 1 0 2 0 0 3 4 2 1 0 0 0 3 3 03:00 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 9

03:15 0 0 0 0 0 0 0 1 0 0 0 0 1 1 0 0 0 0 0 0 0 03:15 2 0 0 0 0 2 2 1 0 0 0 0 1 1 1 0 0 0 0 1 1 5

03:30 0 0 0 0 0 0 0 2 0 0 0 0 2 2 2 0 0 0 0 2 2 03:30 1 0 0 0 0 1 1 0 1 0 0 0 1 1 0 0 0 0 0 0 0 6

03:45 4 0 0 0 0 4 4 0 1 0 0 0 1 1 2 0 0 2 0 4 7 03:45 1 0 0 0 0 1 1 1 1 0 0 0 2 2 0 1 0 0 0 1 1 16

H / T OT 6 0 0 0 0 6 6 4 1 2 0 0 7 8 6 1 0 2 0 9 12 H / T OT 4 0 0 0 0 4 4 2 2 0 0 0 4 4 1 1 0 0 0 2 2 36

PCU's

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Page 9: Appendix 12 · Appendix 12 Traffic Count Results & Drawing LW15-046-02-P-204 For inspection purposes only. Consent of copyright owner required for any other use. EPA Export 22-03-2017:02:09:10.

04:00 1 0 0 0 0 1 1 0 1 0 0 0 1 1 0 1 2 0 0 3 4 04:00 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 0 0 0 0 1 1 7

04:15 2 1 1 0 0 4 5 1 0 0 0 0 1 1 1 0 1 1 0 3 5 04:15 1 0 0 0 0 1 1 0 2 0 0 0 2 2 1 0 0 1 0 2 3 17

04:30 3 0 1 0 0 4 5 0 0 1 0 0 1 2 1 0 0 0 0 1 1 04:30 2 0 0 0 0 2 2 1 0 0 0 0 1 1 2 1 0 1 0 4 5 15

04:45 4 0 0 2 0 6 9 2 0 0 0 0 2 2 4 0 0 0 0 4 4 04:45 4 0 0 1 0 5 6 2 1 0 0 0 3 3 0 0 1 0 0 1 2 25

H / T OT 10 1 2 2 0 15 19 3 1 1 0 0 5 6 6 1 3 1 0 11 14 H / T OT 7 0 0 1 0 8 9 3 3 0 0 0 6 6 4 1 1 2 0 8 11 64

05:00 1 0 0 0 0 1 1 2 1 0 0 0 3 3 1 0 0 2 0 3 6 05:00 0 1 1 0 0 2 3 1 1 2 3 0 7 12 3 0 0 0 0 3 3 27

05:15 2 2 1 1 0 6 8 1 1 3 0 0 5 7 1 0 1 0 0 2 3 05:15 2 0 0 0 0 2 2 0 0 0 0 0 0 0 1 1 2 1 0 5 7 26

05:30 2 1 0 0 0 3 3 7 0 0 0 0 7 7 10 1 1 1 0 13 15 05:30 2 2 0 0 0 4 4 0 0 2 0 0 2 3 1 0 0 1 0 2 3 35

05:45 11 4 0 0 0 15 15 6 2 1 2 0 11 14 6 0 1 0 0 7 8 05:45 3 5 0 0 0 8 8 0 0 2 0 0 2 3 0 0 0 1 0 1 2 50

H / T OT 16 7 1 1 0 25 27 16 4 4 2 0 26 31 18 1 3 3 0 25 30 H / T OT 7 8 1 0 0 16 17 1 1 6 3 0 11 18 5 1 2 3 0 11 16 138

06:00 4 2 2 1 0 9 11 8 1 1 0 0 10 11 1 1 0 1 0 3 4 06:00 1 3 1 1 0 6 8 0 1 0 1 0 2 3 1 1 2 1 0 5 7 45

06:15 4 3 2 2 0 11 15 16 0 1 0 0 17 18 3 1 2 3 0 9 14 06:15 0 0 2 1 0 3 5 0 2 3 2 0 7 11 0 2 0 1 0 3 4 67

06:30 10 3 0 3 0 16 20 25 0 1 1 0 27 29 13 5 1 11 0 30 45 06:30 3 1 1 1 0 6 8 0 4 4 2 0 10 15 1 0 0 2 0 3 6 122

06:45 15 4 1 5 0 25 32 26 1 2 4 0 33 39 14 5 1 9 0 29 41 06:45 2 1 0 2 0 5 8 0 2 2 1 0 5 7 0 1 1 1 0 3 5 132

H / T OT 33 12 5 11 0 61 78 75 2 5 5 0 87 96 31 12 4 24 0 71 104 H / T OT 6 5 4 5 0 20 29 0 9 9 6 0 24 36 2 4 3 5 0 14 22 365

07:00 17 5 1 2 0 25 28 34 5 3 3 0 45 50 9 3 2 5 0 19 27 07:00 4 1 1 1 0 7 9 0 1 0 2 0 3 6 1 0 2 5 0 8 16 135

07:15 5 2 3 1 0 11 14 35 12 3 1 0 51 54 12 6 4 3 0 25 31 07:15 4 2 1 2 0 9 12 1 2 2 3 0 8 13 1 1 1 4 0 7 13 136

07:30 14 7 2 3 0 26 31 61 7 5 3 0 76 82 30 6 7 4 0 47 56 07:30 4 1 1 0 0 6 7 2 3 2 1 0 8 10 1 0 3 5 0 9 17 203

07:45 18 9 4 4 0 35 42 60 6 4 0 0 70 72 49 3 6 3 0 61 68 07:45 7 4 2 0 0 13 14 2 1 1 5 0 9 16 4 4 1 3 0 12 16 229

H / T OT 54 23 10 10 0 97 115 190 30 15 7 0 242 259 100 18 19 15 0 152 181 H / T OT 19 8 5 3 0 35 41 5 7 5 11 0 28 45 7 5 7 17 0 36 62 702

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Page 10: Appendix 12 · Appendix 12 Traffic Count Results & Drawing LW15-046-02-P-204 For inspection purposes only. Consent of copyright owner required for any other use. EPA Export 22-03-2017:02:09:10.

ABACUS TRANSPORTATION SURVEYS ABACUS TRANSPORTATION SURVEYS

CAPPAGH ROAD TRAFFIC COUNTS MAY 2016 CAPPAGH ROAD TRAFFIC COUNTS MAY 2016

MANUAL CLASSIFIED JUNCTION TURNING COUNTS ATH/16/048 MANUAL CLASSIFIED JUNCTION TURNING COUNTS ATH/16/048

SITE: 02 DATE: 18th May 2016 SITE: 02 DATE: 18th May 2016

LOCATION: Cappagh Road (Roundabout 2) DAY: Wednesday LOCATION: Cappagh Road (Roundabout 2) DAY: Wednesday

M OVEM EN T 1 M OVEM EN T 2 M OVEM EN T 3 M OVEM EN T 4 M OVEM EN T 5 M OVEM EN T 6

T IM E C A R S LV OGV1 OGV2 B US T OT P C U C A R S LV OGV1 OGV2 B US T OT P C U C A R S LV OGV1 OGV2 B US T OT P C U T IM E C A R S LV OGV1 OGV2 B US T OT P C U C A R S LV OGV1 OGV2 B US T OT P C U C A R S LV OGV1 OGV2 B US T OT P C U

08:00 22 9 0 8 0 39 49 52 6 2 0 0 60 61 29 4 8 3 0 44 52 08:00 5 1 1 3 0 10 14 0 2 0 1 0 3 4 2 5 5 4 0 16 24 205

08:15 21 2 1 4 0 28 34 63 6 3 3 0 75 80 39 13 1 0 0 53 54 08:15 5 0 1 2 0 8 11 2 2 0 5 0 9 16 6 4 2 7 0 19 29 223

08:30 10 8 2 4 0 24 30 55 4 2 2 0 63 67 35 5 3 2 0 45 49 08:30 3 3 0 0 0 6 6 5 3 1 4 0 13 19 4 3 1 5 0 13 20 191

08:45 29 2 0 1 0 32 33 77 10 2 3 0 92 97 37 7 7 1 0 52 57 08:45 4 1 1 2 0 8 11 5 2 1 3 0 11 15 10 5 1 6 0 22 30 244

H / T OT 82 21 3 17 0 123 147 247 26 9 8 0 290 305 140 29 19 6 0 194 211 H / T OT 17 5 3 7 0 32 43 12 9 2 13 0 36 54 22 17 9 22 0 70 103 862

09:00 22 4 2 5 0 33 41 56 14 5 6 0 81 91 38 10 6 3 3 60 70 09:00 8 1 0 2 0 11 14 3 3 0 3 0 9 13 8 3 1 5 0 17 24 252

09:15 22 3 3 7 0 35 46 23 5 1 0 0 29 30 20 10 5 4 1 40 49 09:15 6 3 2 2 0 13 17 2 1 1 3 0 7 11 9 4 3 1 0 17 20 172

09:30 10 6 0 7 0 23 32 31 8 5 2 0 46 51 17 3 3 0 1 24 27 09:30 5 0 1 3 0 9 13 9 3 1 3 0 16 20 6 4 5 5 0 20 29 173

09:45 17 4 1 3 0 25 29 24 5 2 4 0 35 41 21 3 4 4 2 34 43 09:45 6 2 0 1 0 9 10 6 4 1 3 0 14 18 9 4 2 3 0 18 23 165

H / T OT 71 17 6 22 0 116 148 134 32 13 12 0 191 213 96 26 18 11 7 158 188 H / T OT 25 6 3 8 0 42 54 20 11 3 12 0 46 63 32 15 11 14 0 72 96 762

10:00 8 6 1 10 0 25 39 25 11 7 2 0 45 51 13 8 5 2 0 28 33 10:00 8 1 1 6 0 16 24 2 4 1 4 0 11 17 10 7 1 5 0 23 30 194

10:15 8 2 1 6 0 17 25 13 8 3 2 0 26 30 19 6 7 4 0 36 45 10:15 3 3 2 3 0 11 16 6 2 1 2 0 11 14 10 2 1 4 0 17 23 153

10:30 11 1 6 5 0 23 33 16 13 4 3 0 36 42 24 6 4 2 0 36 41 10:30 5 5 0 4 0 14 19 7 2 2 4 0 15 21 5 3 2 6 0 16 25 180

10:45 16 5 1 5 0 27 34 14 8 2 4 0 28 34 18 9 5 3 0 35 41 10:45 6 3 0 1 0 10 11 6 2 1 3 0 12 16 11 4 3 3 0 21 26 164

H / T OT 43 14 9 26 0 92 130 68 40 16 11 0 135 157 74 29 21 11 0 135 160 H / T OT 22 12 3 14 0 51 71 21 10 5 13 0 49 68 36 16 7 18 0 77 104 690

11:00 10 4 2 6 0 22 31 21 6 4 3 0 34 40 28 2 1 1 2 34 38 11:00 2 2 1 3 0 8 12 5 5 1 2 0 13 16 11 2 3 4 0 20 27 164

11:15 8 5 1 6 0 20 28 15 7 4 4 0 30 37 15 10 2 5 0 32 40 11:15 6 3 1 0 0 10 11 3 6 2 3 0 14 19 8 3 2 4 0 17 23 158

11:30 9 7 3 7 0 26 37 15 7 2 2 0 26 30 17 9 4 2 1 33 39 11:30 6 5 1 4 0 16 22 5 6 2 5 0 18 26 11 2 3 4 0 20 27 179

11:45 11 2 0 4 0 17 22 12 5 5 4 0 26 34 17 10 5 2 0 34 39 11:45 6 4 0 3 0 13 17 8 2 2 5 0 17 25 9 2 0 4 0 15 20 157

H / T OT 38 18 6 23 0 85 118 63 25 15 13 0 116 140 77 31 12 10 3 133 155 H / T OT 20 14 3 10 0 47 62 21 19 7 15 0 62 85 39 9 8 16 0 72 97 657

PCU's

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Page 11: Appendix 12 · Appendix 12 Traffic Count Results & Drawing LW15-046-02-P-204 For inspection purposes only. Consent of copyright owner required for any other use. EPA Export 22-03-2017:02:09:10.

12:00 12 4 0 2 0 18 21 14 10 11 0 0 35 41 21 7 6 6 0 40 51 12:00 7 1 1 3 0 12 16 6 5 1 1 0 13 15 18 10 2 7 0 37 47 190

12:15 6 9 4 4 0 23 30 16 10 4 6 0 36 46 26 5 4 3 0 38 44 12:15 2 4 2 4 0 12 18 8 4 0 3 0 15 19 7 7 0 0 0 14 14 171

12:30 12 6 3 3 0 24 29 22 6 3 4 0 35 42 29 6 1 5 0 41 48 12:30 2 1 0 1 0 4 5 3 2 0 6 0 11 19 13 5 1 2 0 21 24 167

12:45 16 6 1 8 0 31 42 24 6 2 4 0 36 42 19 3 10 4 0 36 46 12:45 8 1 0 1 0 10 11 8 1 3 5 0 17 25 11 3 3 2 0 19 23 190

H / T OT 46 25 8 17 0 96 122 76 32 20 14 0 142 170 95 21 21 18 0 155 189 H / T OT 19 7 3 9 0 38 51 25 12 4 15 0 56 78 49 25 6 11 0 91 108 718

13:00 19 8 2 4 0 33 39 26 10 1 6 0 43 51 21 8 6 3 1 39 47 13:00 8 0 1 3 0 12 16 7 0 2 3 0 12 17 17 3 3 4 0 27 34 204

13:15 10 2 1 4 0 17 23 13 9 3 3 1 29 35 19 6 1 6 0 32 40 13:15 4 4 1 2 0 11 14 4 4 0 3 0 11 15 16 5 1 3 0 25 29 157

13:30 13 5 1 5 0 24 31 13 5 3 8 0 29 41 13 7 3 4 0 27 34 13:30 4 1 1 4 0 10 16 5 1 0 2 0 8 11 11 4 1 3 0 19 23 155

13:45 10 1 3 9 0 23 36 19 3 2 3 0 27 32 26 7 3 6 0 42 51 13:45 8 2 0 2 0 12 15 9 3 2 4 0 18 24 26 2 1 6 0 35 43 202

H / T OT 52 16 7 22 0 97 129 71 27 9 20 1 128 160 79 28 13 19 1 140 172 H / T OT 24 7 3 11 0 45 61 25 8 4 12 0 49 67 70 14 6 16 0 106 130 718

14:00 11 3 2 5 0 21 29 22 5 3 4 0 34 41 26 7 8 4 0 45 54 14:00 2 3 0 5 0 10 17 9 1 0 5 0 15 22 14 0 1 6 0 21 29 191

14:15 11 3 1 4 0 19 25 18 11 5 2 1 37 43 22 2 5 2 0 31 36 14:15 3 3 1 1 0 8 10 5 1 0 5 0 11 18 14 2 2 3 0 21 26 157

14:30 5 8 2 4 0 19 25 16 8 7 1 0 32 37 27 10 5 4 0 46 54 14:30 3 3 1 7 0 14 24 4 4 0 3 0 11 15 17 2 1 3 0 23 27 182

14:45 8 3 1 3 0 15 19 19 3 6 3 0 31 38 24 5 3 1 1 34 38 14:45 1 4 2 3 0 10 15 3 2 1 3 0 9 13 9 5 2 3 0 19 24 147

H / T OT 35 17 6 16 0 74 98 75 27 21 10 1 134 159 99 24 21 11 1 156 182 H / T OT 9 13 4 16 0 42 65 21 8 1 16 0 46 67 54 9 6 15 0 84 107 677

15:00 7 6 1 6 0 20 28 15 6 7 3 0 31 38 29 7 10 3 0 49 58 15:00 5 3 0 2 0 10 13 2 2 1 3 0 8 12 10 2 2 3 0 17 22 172

15:15 6 6 4 5 0 21 30 14 8 2 2 0 26 30 26 5 4 5 0 40 49 15:15 2 1 1 3 0 7 11 3 2 2 4 0 11 17 9 3 2 4 0 18 24 160

15:30 5 5 4 7 0 21 32 16 8 10 6 1 41 55 26 12 4 3 0 45 51 15:30 0 1 0 3 0 4 8 2 3 0 4 0 9 14 7 3 2 4 0 16 22 182

15:45 9 3 0 8 0 20 30 8 7 0 8 0 23 33 39 7 4 3 0 53 59 15:45 5 0 1 8 0 14 25 9 1 1 4 0 15 21 13 5 3 2 0 23 27 195

H / T OT 27 20 9 26 0 82 120 53 29 19 19 1 121 156 120 31 22 14 0 187 216 H / T OT 12 5 2 16 0 35 57 16 8 4 15 0 43 65 39 13 9 13 0 74 95 709

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Page 12: Appendix 12 · Appendix 12 Traffic Count Results & Drawing LW15-046-02-P-204 For inspection purposes only. Consent of copyright owner required for any other use. EPA Export 22-03-2017:02:09:10.

ABACUS TRANSPORTATION SURVEYS ABACUS TRANSPORTATION SURVEYS

CAPPAGH ROAD TRAFFIC COUNTS MAY 2016 CAPPAGH ROAD TRAFFIC COUNTS MAY 2016

MANUAL CLASSIFIED JUNCTION TURNING COUNTS ATH/16/048 MANUAL CLASSIFIED JUNCTION TURNING COUNTS ATH/16/048

SITE: 02 DATE: 18th May 2016 SITE: 02 DATE: 18th May 2016

LOCATION: Cappagh Road (Roundabout 2) DAY: Wednesday LOCATION: Cappagh Road (Roundabout 2) DAY: Wednesday

M OVEM EN T 1 M OVEM EN T 2 M OVEM EN T 3 M OVEM EN T 4 M OVEM EN T 5 M OVEM EN T 6

T IM E C A R S LV OGV1 OGV2 B US T OT P C U C A R S LV OGV1 OGV2 B US T OT P C U C A R S LV OGV1 OGV2 B US T OT P C U T IM E C A R S LV OGV1 OGV2 B US T OT P C U C A R S LV OGV1 OGV2 B US T OT P C U C A R S LV OGV1 OGV2 B US T OT P C U

16:00 6 0 2 6 0 14 23 17 8 0 4 1 30 36 46 9 2 8 0 65 76 16:00 5 0 1 2 0 8 11 5 2 0 5 0 12 19 18 6 2 8 0 34 45 210

16:15 5 1 2 0 0 8 9 19 5 2 3 0 29 34 38 9 3 2 0 52 56 16:15 2 3 1 1 0 7 9 6 2 1 4 0 13 19 9 5 1 3 0 18 22 149

16:30 6 4 2 3 0 15 20 26 8 4 7 1 46 58 48 17 2 0 0 67 68 16:30 3 0 0 1 0 4 5 11 3 0 2 0 16 19 19 1 1 2 0 23 26 196

16:45 10 2 0 2 0 14 17 34 11 3 5 0 53 61 63 4 2 3 0 72 77 16:45 4 0 0 2 0 6 9 3 3 0 1 0 7 8 15 3 1 3 0 22 26 198

H / T OT 27 7 6 11 0 51 68 96 32 9 19 2 158 189 195 39 9 13 0 256 277 H / T OT 14 3 2 6 0 25 34 25 10 1 12 0 48 64 61 15 5 16 0 97 120 753

17:00 6 2 0 2 0 10 13 59 11 1 1 0 72 74 88 10 6 3 0 107 114 17:00 1 0 0 1 0 2 3 10 0 1 3 0 14 18 36 9 0 1 0 46 47 269

17:15 1 2 0 3 0 6 10 51 6 5 2 0 64 69 76 8 2 0 0 86 87 17:15 2 1 0 4 0 7 12 3 1 0 2 0 6 9 17 3 0 2 0 22 25 211

17:30 3 2 0 1 0 6 7 64 4 5 2 0 75 80 90 6 3 0 0 99 101 17:30 1 1 0 3 0 5 9 7 3 0 1 0 11 12 22 4 0 2 0 28 31 240

17:45 2 0 0 2 0 4 7 37 2 3 3 0 45 50 47 7 1 1 0 56 58 17:45 0 1 0 0 0 1 1 3 1 0 1 0 5 6 4 2 0 0 0 6 6 128

H / T OT 12 6 0 8 0 26 36 211 23 14 8 0 256 273 301 31 12 4 0 348 359 H / T OT 4 3 0 8 0 15 25 23 5 1 7 0 36 46 79 18 0 5 0 102 109 849

18:00 3 0 0 4 0 7 12 20 4 0 0 0 24 24 62 10 1 0 0 73 74 18:00 2 0 0 4 0 6 11 6 1 0 0 0 7 7 16 2 0 0 0 18 18 146

18:15 1 0 0 3 0 4 8 23 1 3 0 0 27 29 45 4 1 1 0 51 53 18:15 2 0 0 0 0 2 2 4 2 0 1 0 7 8 5 1 0 4 0 10 15 115

18:30 3 1 0 0 0 4 4 11 2 0 1 0 14 15 28 4 2 1 0 35 37 18:30 1 0 0 0 0 1 1 2 0 0 0 0 2 2 13 0 0 1 0 14 15 75

18:45 3 2 0 1 0 6 7 20 3 2 3 0 28 33 36 3 1 0 0 40 41 18:45 0 0 0 1 0 1 2 2 0 0 0 0 2 2 5 1 0 0 0 6 6 91

H / T OT 10 3 0 8 0 21 31 74 10 5 4 0 93 101 171 21 5 2 0 199 204 H / T OT 5 0 0 5 0 10 17 14 3 0 1 0 18 19 39 4 0 5 0 48 55 427

19:00 1 0 1 3 0 5 9 15 2 0 1 0 18 19 28 7 1 0 0 36 37 19:00 0 0 0 0 0 0 0 1 0 0 0 0 1 1 10 2 0 0 0 12 12 78

19:15 0 0 1 0 0 1 2 5 1 3 1 0 10 13 24 2 3 1 1 31 35 19:15 0 0 0 0 0 0 0 1 0 0 0 0 1 1 2 1 0 0 0 3 3 53

19:30 2 1 0 1 0 4 5 7 1 0 0 0 8 8 20 2 1 2 0 25 28 19:30 0 0 0 0 0 0 0 3 0 0 0 0 3 3 4 0 0 0 0 4 4 48

19:45 0 0 0 0 0 0 0 9 0 1 0 0 10 11 6 1 1 0 0 8 9 19:45 1 0 0 0 0 1 1 1 0 0 0 0 1 1 2 1 0 0 0 3 3 24

H / T OT 3 1 2 4 0 10 16 36 4 4 2 0 46 51 78 12 6 3 1 100 108 H / T OT 1 0 0 0 0 1 1 6 0 0 0 0 6 6 18 4 0 0 0 22 22 204

PCU's

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20:00 1 1 0 0 0 2 2 8 2 0 0 0 10 10 15 1 2 0 2 20 23 20:00 2 1 0 0 0 3 3 1 0 0 0 0 1 1 5 0 0 0 0 5 5 44

20:15 3 1 0 0 0 4 4 4 0 0 0 0 4 4 10 1 0 0 0 11 11 20:15 0 0 0 0 0 0 0 0 0 0 0 0 0 0 3 0 0 0 0 3 3 22

20:30 0 0 0 0 0 0 0 5 0 0 2 0 7 10 10 0 0 1 0 11 12 20:30 0 0 0 0 0 0 0 0 0 0 0 0 0 0 4 1 0 0 0 5 5 27

20:45 1 0 0 0 0 1 1 7 1 1 0 0 9 10 15 1 1 1 0 18 20 20:45 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 30

H / T OT 5 2 0 0 0 7 7 24 3 1 2 0 30 33 50 3 3 2 2 60 66 H / T OT 2 1 0 0 0 3 3 1 0 0 0 0 1 1 12 1 0 0 0 13 13 123

21:00 1 0 1 0 0 2 3 4 1 0 0 0 5 5 14 0 0 0 0 14 14 21:00 0 0 0 0 0 0 0 1 1 0 0 0 2 2 1 1 0 0 0 2 2 26

21:15 0 0 0 0 0 0 0 3 4 0 0 0 7 7 5 1 0 0 0 6 6 21:15 1 0 0 0 0 1 1 0 0 0 0 0 0 0 1 1 0 0 0 2 2 16

21:30 0 1 0 0 0 1 1 2 0 1 1 0 4 6 9 3 0 1 0 13 14 21:30 0 0 0 0 0 0 0 1 0 0 0 0 1 1 0 0 1 0 0 1 2 24

21:45 1 0 0 0 0 1 1 2 1 0 0 0 3 3 7 2 0 1 0 10 11 21:45 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 1 0 0 2 3 18

H / T OT 2 1 1 0 0 4 5 11 6 1 1 0 19 21 35 6 0 2 0 43 46 H / T OT 1 0 0 0 0 1 1 2 1 0 0 0 3 3 2 3 2 0 0 7 8 83

22:00 0 0 0 0 0 0 0 3 0 0 0 0 3 3 1 0 0 0 0 1 1 22:00 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 4

22:15 0 0 0 0 0 0 0 0 0 0 1 0 1 2 2 0 0 0 0 2 2 22:15 0 1 0 0 0 1 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 5

22:30 2 0 0 0 0 2 2 2 0 0 0 0 2 2 0 0 0 0 0 0 0 22:30 2 1 0 0 0 3 3 0 1 0 0 0 1 1 0 0 0 0 0 0 0 8

22:45 3 1 0 1 0 5 6 2 0 0 1 0 3 4 2 0 1 0 0 3 4 22:45 1 0 0 0 0 1 1 3 0 0 0 0 3 3 0 0 0 0 0 0 0 18

H / T OT 5 1 0 1 0 7 8 7 0 0 2 0 9 12 5 0 1 0 0 6 7 H / T OT 3 2 0 0 0 5 5 3 1 0 0 0 4 4 0 0 0 0 0 0 0 35

23:00 1 0 0 0 0 1 1 1 0 0 0 0 1 1 1 0 0 0 0 1 1 23:00 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 0 0 1 2 5

23:15 0 1 0 1 0 2 3 1 0 0 0 0 1 1 3 0 0 0 0 3 3 23:15 1 0 0 0 0 1 1 1 0 0 0 0 1 1 0 0 0 0 0 0 0 9

23:30 0 1 0 0 0 1 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 23:30 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1

23:45 0 1 0 0 0 1 1 4 0 0 0 0 4 4 0 0 0 0 0 0 0 23:45 0 0 0 0 0 0 0 1 1 0 0 0 2 2 1 1 0 0 0 2 2 9

H / T OT 1 3 0 1 0 5 6 6 0 0 0 0 6 6 4 0 0 0 0 4 4 H / T OT 1 0 0 0 0 1 1 2 1 0 0 0 3 3 1 1 1 0 0 3 4 240 0 :0 0 -

0 0 :0 0583 217 82 227 0 1109 1445 1549 354 184 161 5 2253 2559 1789 364 212 176 15 2556 2906

0 0 :0 0 -

0 0 :0 0223 99 36 120 0 478 652 249 132 52 153 0 586 811 577 179 83 178 0 1017 1290 9663

0 6 :0 0 -

2 2 :0 0540 203 78 221 0 1042 1368 1504 348 176 155 5 2188 2483 1741 361 205 165 15 2487 2819

0 6 :0 0 -

2 2 :0 0200 89 35 118 0 442 613 237 120 46 148 0 551 766 561 172 79 173 0 985 1249 9299

0 7:0 0 -

19 :0 0497 187 70 206 0 960 1263 1358 333 165 145 5 2006 2282 1547 328 192 134 12 2213 2495

0 7:0 0 -

19 :0 0190 83 31 113 0 417 579 228 110 37 142 0 517 720 527 160 74 168 0 929 1184 8524

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81.80m

81.80m

18.640

3.64

02.99

93.64

0

17.900

3.60

0

3.60

0

WeighBridge In

WeighBridge Out

82.90m

2.20

0

XX

FFL = 82.90m

Weighbridge

Building

1

.

5

0

m

R10.00m

CAPPAGH Road

C

A

P

P

A

G

H

R

O

A

D

1

2

.

3

0

m

7

.

2

0

m

1

0

.

0

0

m

2

5

.

0

0

m

12.300

Twin Leaf Heavy Duty Galvanised

Lockable Steel Gates

2.40

0

2.97

5

ORIGINAL DRAWING SIZE A1 - (841 x 594)

A

Sheet FTC-A1-2015 rev. A (template filed in O:Acad\Templates\Autocad) (Dec 2015) - template externally referenced

1

Rev

.

Ap

p'd

Dra

wn

Ch

k'd

Description

Name of Client

Name of Job

Title of Drawing

Scales Used

Dwg. No. Rev.

Use figured dimensions only.on the project for which the document was originally issued.of Fehily Timoney & Company as copyright holder except as agreed for useor stored in any retrieval system of any nature without the written permissionNo part of this document may be reproduced or transmitted in any form

Do not scale. If in doubt - Ask!

Revision History

CONSULTANTS INENGINEERING &ENVIRONMENTALSCIENCES

Date

Rev Origin

NOT FOR CONSTRUCTION UNLESS SPECIFICALLY STATED OTHERWISE

(Sean Keohane)

W: www.fehilytimoney.ie, E: [email protected]

T:+353-21-4964133, F:+353-21-4964464Core House, Pouladuff Rd, Cork, Ireland.

T:+353-1-6583500, F:+353-1-6583501

J5 Plaza, North Park Business Park,North Road, Dublin 11, Ireland

2 3 4 5

B

C

D

A

B

C

D

1 2 3 4 5

This Drawing was printed toA1-

FLOOR PLAN####

ORIGINAL DRAWING SIZE A1 - (841 x 594) SCALE HORIZ.10020 5010010

Rev

.

Ap

p'd

Dra

wn

Ch

k'd

Description

Name of Client

Name of Job

Title of Drawing

Scales Used

Dwg. No. Rev.

Use figured dimensions only. on the project for which the document was originally issued.of Fehily Timoney & Company as copyright holder except as agreed for useor stored in any retrieval system of any nature without the written permissionNo part of this document may be reproduced or transmitted in any form

Do not scale. If in doubt - Ask!

1010

020

50SC

ALE

- VE

RTICAL

100

Revision History

Date

Rev Origin

NOT FOR CONSTRUCTION UNLESS SPECIFICALLY STATED OTHERWISE

PROPOSED MATERIALS PROCESSING& TRANSFER FACILTY

AT MILLENNIUM BUSINESS PARK

WEIGHBRIDGE ANDENTRANCE DETAIL

LW15-046-02-P-204O:\ACAD\2015\LW15\046\02\LW1504602_P-204

1:100

When Applicable : Ordnance Survey Ireland Licence No. EN 0001216 © Ordnance Survey Ireland and Government of Ireland

C

A B C PLANNING

FLOOR PLAN100

0m 1m 2m 3m 4m 5m 6m 7m 8m 9m 10m

Scale 1:100

CorkA SK D

MBG Oct.2016 Issue For Planning Application

CORKB SK D

MBG Nov.2016 Issue For Planning Application

CORKC SK D

MBG Dec.2016 Issue For Planning Application

T:\Xphotos\LOGO\Thorntons logo red_500px.BMP

PLAN

EAST ELEVATION

WEST ELEVATION

NORTH ELEVATION

SOUTH ELEVATION

TYPICAL CROSS SECTION

PROPOSED NEW SITE ENTRANCE AT CAPPAGH ROAD

(Scale 1:200)

(Refer To Dwg P-003 For Full Site Plan)

EXTERNAL ELEVATION OF NEW ENTRANCE GATES FROM CAPPAGH ROAD

E

L

E

V

A

T

I

O

N

RECEPTION BUILDING

FOOTPATH and CYCLE LANE

· Footpath and Cycle Lane

To Be Constructed Across

Obsolete Entrances

· Tactile Paving to Both

Sides Of New Entrance.

· New Cycle Lane Sign,

Both Sides of New

Entrance.

RIGHT TURN LANE

· Right turn Lane To TD41-42/11

· Road Markings to TSRM and TD41-42/11

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Page 15: Appendix 12 · Appendix 12 Traffic Count Results & Drawing LW15-046-02-P-204 For inspection purposes only. Consent of copyright owner required for any other use. EPA Export 22-03-2017:02:09:10.

Appendix 13

PICADY Analysis Results

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Page 16: Appendix 12 · Appendix 12 Traffic Count Results & Drawing LW15-046-02-P-204 For inspection purposes only. Consent of copyright owner required for any other use. EPA Export 22-03-2017:02:09:10.

Run Analysis

Arm Names and Flow Scaling Factors

Stream Labelling Convention

Stream A-B contains traffic going from A to B etc.

Run Information

PICADYGUI Version: 5.1 AE

Analysis Program Release: 5.0 (MAY 2010)

© Copyright TRL Limited, 2010 Adapted from PICADY/3 which is Crown Copyright by permission of the controller of HMSO

For sales and distribution information, program advice and maintenance, contact:TRL Limited

Crowthorne HouseNine Mile Ride

Wokingham, Berks.RG40 3GA, UK

Tel: +44 (0)1344 770758Fax:+44 (0)1344 770864E-mail: [email protected]

Web: www.trlsoftware.co.uk

The user of this computer program for the solution of an engineering problem is in no way relieved of their responsibility for the correctness of the solution

Parameter ValuesFile Run Q:\2015\LW15\046\02\PICADY\LW1504602_Millennium Park.vpiDate Run 15 September 2016Time Run 12:12:23Driving Side Drive On The Left

Arm Arm Name Flow Scaling Factor(%)

Arm A Southbound 100Arm B Entrance 100Arm C Northbound 100

Parameter ValuesRun Title LW1504602_Millennium ParkLocation DublinDate 13 September 2016Enumerator seamaso [DSKCORK109]Job Number LW1504602Status -Client -Description -

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Errors and Warnings

Geometric Data

Geometric Parameters

Slope and Intercept Values

Note: Streams may be combined in which case capacity will be adjusted These values do not allow for any site-specific corrections

Parameter ValuesWarning No Errors Or Warnings

Parameter Minor Arm BMajor Road Carriageway Width (m) 9.00Major Road Kerbed Central Reserve Width (m) 0.00Major Road Right Turning Lane Width (m) 3.00Minor Road First Lane Width (m) 4.00Minor Road Visibility To Right (m) 160Minor Road Visibility To Left (m) 160Major Road Right Turn Visibility (m) 70Major Road Right Turn Blocks Traffic Yes (if over 1 veh)

StreamIntercept

forStream

SlopeforA-B

SlopeforA-C

SlopeforC-A

SlopeforC-B

B-A 674.969 0.107 0.270 0.170 0.386B-C 797.213 0.106 0.269 - -C-B 668.004 0.225 0.225 - -

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Junction Diagram

Demand Data

Modelling Periods

Parameter Period Duration(min)

Segment Length(min)

First Modelling Period 17:00-18:00 60 15

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Direct Entry Flows

Demand Set: LW1504602_Millennium ParkModelling Period: 17:00-18:00

Segment: 17:00-17:15

Segment: 17:15-17:30

Segment: 17:30-17:45

Segment: 17:45-18:00

Turning Counts

Demand Set: LW1504602_Millennium ParkModelling Period: 17:00-18:00

Segment: 17:00-17:15

Arm Flow(veh/interval)

Arm A 89.00Arm B 3.00Arm C 101.00

Arm Flow(veh/interval)

Arm A 75.00Arm B 2.00Arm C 90.00

Arm Flow(veh/interval)

Arm A 85.00Arm B 3.00Arm C 100.00

Arm Flow(veh/interval)

Arm A 51.00Arm B 2.00Arm C 51.00

From/To Arm A Arm B Arm CArm A - 0 89Arm B 2 - 1Arm C 98 3 -

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Segment: 17:15-17:30

Segment: 17:30-17:45

Segment: 17:45-18:00

Turning proportions are calculated from turning count data

Turning Proportions

Demand Set: LW1504602_Millennium ParkModelling Period: 17:00-18:00

Segment: 17:00-17:15

Segment: 17:15-17:30

From/To Arm A Arm B Arm CArm A - 0 75Arm B 1 - 1Arm C 88 2 -

From/To Arm A Arm B Arm CArm A - 0 85Arm B 2 - 1Arm C 97 3 -

From/To Arm A Arm B Arm CArm A - 0 51Arm B 1 - 1Arm C 49 2 -

From/To Arm A Arm B Arm CArm A 0.000 0.000 1.000Arm B 0.667 0.000 0.333Arm C 0.970 0.030 0.000

From/To Arm A Arm B Arm CArm A 0.000 0.000 1.000Arm B 0.500 0.000 0.500Arm C 0.978 0.022 0.000

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Segment: 17:30-17:45

Segment: 17:45-18:00

Heavy Vehicles Percentages

Demand Set: LW1504602_Millennium ParkModelling Period: 17:00-18:00

From/To Arm A Arm B Arm CArm A 0.000 0.000 1.000Arm B 0.667 0.000 0.333Arm C 0.970 0.030 0.000

From/To Arm A Arm B Arm CArm A 0.000 0.000 1.000Arm B 0.500 0.000 0.500Arm C 0.961 0.039 0.000

From/To Arm A Arm B Arm CArm A - 0.0 10.0Arm B 100.0 - 100.0Arm C 7.0 100.0 -

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Queue Diagrams

Demand Set: Sum of Demand Sets for Modelling Period: 17:00 - 18:00 Modelling Period: 17:00-18:00 View Extent: 40m

Queue Interval 1: 17:00-17:15 Queue Interval 2: 17:15-17:30

Queue Interval 3: 17:30-17:45 Queue Interval 4: 17:45-18:00

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Demand Data Graph

Demand Set: LW1504602_Millennium Park Modelling Period: 17:00-18:00

Capacity Graph

Demand Set: Sum of Demand Sets for Modelling Period: 17:00 - 18:00Modelling Period: 17:00-18:00

RFC Graph

Demand Set: Sum of Demand Sets for Modelling Period: 17:00 - 18:00Modelling Period: 17:00-18:00

Start Queue Graph

Demand Set: Sum of Demand Sets for Modelling Period: 17:00 - 18:00Modelling Period: 17:00-18:00

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End Queue Graph

Demand Set: Sum of Demand Sets for Modelling Period: 17:00 - 18:00Modelling Period: 17:00-18:00

Delay Graph

Demand Set: Sum of Demand Sets for Modelling Period: 17:00 - 18:00Modelling Period: 17:00-18:00

Queues & Delays

Demand Set: Sum of Demand Sets for Modelling Period: 17:00 - 18:00Modelling Period: 17:00-18:00

Segment Stream Demand(veh/min)

Capacity(veh/min) RFC

Ped.Flow

(ped/min)

Start Queue(veh)

End Queue(veh)

Geometric Delay

(veh.min/segment)

Delay(veh.min/segment)

Mean ArrivingVehicle Delay(min)

17:00-17:15

B-AC 0.20 4.51 0.044 - 0.00 0.05 - 0.6 0.23C-AB 0.20 4.83 0.041 - 0.00 0.04 - 0.7 0.22C-A - - - - - - - - -A-B 0.00 - - - - - - - -A-C 5.93 - - - - - - - -

Segment Stream Demand(veh/min)

Capacity(veh/min) RFC

Ped.Flow

(ped/min)

Start Queue(veh)

End Queue(veh)

Geometric Delay

(veh.min/segment)

Delay(veh.min/segment)

Mean ArrivingVehicle Delay(min)

17:15-17:30

B-AC 0.13 4.97 0.027 - 0.05 0.03 - 0.4 0.21C-AB 0.13 4.95 0.027 - 0.04 0.03 - 0.4 0.21C-A - - - - - - - - -A-B 0.00 - - - - - - - -A-C 5.00 - - - - - - - -

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Entry capacities marked with an '(X)' are dominated by a pedestrian crossing in that time segment.In time segments marked with a '(B)', traffic leaving the junction may block back from a crossing so impairing normal operation of the junction.Delays marked with '##' could not be calculated.

Overall Queues & Delays

Queueing Delay Information Over Whole Period

Demand Set: Sum of Demand Sets for Modelling Period: 17:00 - 18:00Modelling Period: 17:00-18:00

Delay is that occurring only within the time period.Inclusive delay includes delay suffered by vehicles which are still queuing after the end of the time period.These will only be significantly different if there is a large queue remaining at the end of the time period.

PICADY 5 Run Successful

Segment Stream Demand(veh/min)

Capacity(veh/min) RFC

Ped.Flow

(ped/min)

Start Queue(veh)

End Queue(veh)

Geometric Delay

(veh.min/segment)

Delay(veh.min/segment)

Mean ArrivingVehicle Delay(min)

17:30-17:45

B-AC 0.20 4.56 0.044 - 0.03 0.05 - 0.7 0.23C-AB 0.20 4.87 0.041 - 0.03 0.04 - 0.7 0.21C-A - - - - - - - - -A-B 0.00 - - - - - - - -A-C 5.67 - - - - - - - -

Segment Stream Demand(veh/min)

Capacity(veh/min) RFC

Ped.Flow

(ped/min)

Start Queue(veh)

End Queue(veh)

Geometric Delay

(veh.min/segment)

Delay(veh.min/segment)

Mean ArrivingVehicle Delay(min)

17:45-18:00

B-AC 0.13 5.36 0.025 - 0.05 0.03 - 0.4 0.19C-AB 0.13 5.15 0.026 - 0.04 0.03 - 0.4 0.20C-A - - - - - - - - -A-B 0.00 - - - - - - - -A-C 3.40 - - - - - - - -

Stream Total Demand(veh)

Total Demand(veh/h)

Queueing Delay(min)

Queueing Delay(min/veh)

Inclusive Delay(min)

Inclusive Delay(min/veh)

B-AC 10.0 10.0 2.1 0.2 2.1 0.2C-AB 10.0 10.0 2.2 0.2 2.2 0.2C-A - - - - - -A-B 0.0 0.0 - - - -A-C 300.0 300.0 - - - -All 652.0 652.0 4.3 0.0 4.3 0.0

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Appendix 14

Sound Level Meter Calibration Certificate

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Appendix 15

Coordinates of Noise Sensitive Locations

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Receptor

Location Description Easting Northing

R1 Café 710167 740822

R2 Single Storey Dwelling 710543 740421

R3 Single Storey Dwelling 710786 740120

R4 Single Storey Dwelling 710793 740111

R5 Single Storey Dwelling 710797 740090

R6 Single Storey Dwelling 710800 740083

R7 Single Storey Dwelling 710806 740065

R8 Single Storey Dwelling 710809 740056

R9 Single Storey Dwelling 710814 740040

R10 Single Storey Dwelling 710817 740031

R11 Single Storey Dwelling 710828 740014

R12 Single Storey Dwelling 710829 740003

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Appendix 16

NPWS Site Synopses

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SITE SYNOPSIS

Version date: 12.08.2013 1 of 2 000199_Rev13.Doc

Site Name: Baldoyle Bay SAC Site Code: 000199 Baldoyle Bay SAC extends from just below Portmarnock village to the west pier at Howth in Co. Dublin. It is a tidal estuarine bay protected from the open sea by a large sand-dune system. Two small rivers, the Mayne and the Sluice, flow into the bay. The site is a Special Area of Conservation (SAC) selected for the following habitats and/or species listed on Annex I / II of the E.U. Habitats Directive (* = priority; numbers in brackets are Natura 2000 codes):

[1140] Tidal Mudflats and Sandflats [1310] Salicornia Mud [1330] Atlantic Salt Meadows [1410] Mediterranean Salt Meadows

Large areas of intertidal flats are exposed at low tide at this site. These are mostly sands but grade to muds in the inner sheltered parts of the estuary. Extensive areas of Common Cord-grass (Spartina anglica) occur in the inner estuary. Both the Narrow-leaved Eelgrass (Zostera angustifolia) and the Dwarf Eelgrass (Z. noltii) are also found here. During summer, the sandflats of the sheltered areas are covered by mats of green algae (Enteromorpha spp. and Ulva lactuca). The sediments have a typical macrofauna, with Lugworm (Arenicola marina) dominating the sandy flats. The tubeworm Lanice conchilega is present in high densities at the low tide mark and the small gastropod Hydrobia ulvae occurs in the muddy areas, along with the crustacean Corophium volutator. Areas of saltmarsh occur near Portmarnock Bridge and at Portmarnock Point, with narrow strips along other parts of the estuary. Species such as glassworts (Salicornia spp.), Sea-purslane (Halimione portulacoides), Sea Plantain (Plantago maritima) and Sea Rush (Juncus maritimus) are found here. Portmarnock Spit formerly had a well-developed sand dune system but this has been largely replaced by golf courses and is mostly excluded from the site. A few dune hills are still intact at Portmarnock Point, and there are small dune hills east of Cush Point and below the Claremont Hotel. These are mostly dominated by Marram (Ammophila arenaria), though Lyme-grass (Leymus arenarius) is also found. The site includes a brackish marsh along the Mayne River. Soils here have a high organic content and are poorly drained, and some pools occur. Rushes (Juncus spp.) and salt tolerant species such as Common Scurvygrass (Cochleria officinalis) and

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Greater Sea-spurrey (Spergularia media) are typical of this area. Knotted Hedge-parsley (Torilis nodosa), a scarce plant in eastern Ireland, has been recorded here, along with Brackish Water-crowfoot (Ranunculus baudotti), a species of brackish pools and ditches which has declined in most places due to habitat loss. Two plant species, legally protected under the Flora (Protection) Order, 1999, occur in the Mayne marsh, Borrer's Saltmarsh-grass (Puccinellia fasciculata) and Meadow Barley (Hordeum secalinum). Baldoyle Bay is an important bird site for wintering waterfowl and the inner part of the estuary is a Special Protection Area under the E.U. Birds Directive as well as being a Statutory Nature Reserve. Internationally important numbers of Pale-bellied Brent Goose (418) and nationally important numbers of two Annex I Birds Directive species - Golden Pover (1,900) and Bar-tailed Godwit (283) - have been recorded. Four other species also reached nationally important numbers: Shelduck (147), Pintail (26), Grey Plover (148) and Ringed Plover (218) - all figures are average peaks for four winters 1994/95 to 1997/1998. Breeding wetland birds at the site include Shelduck, Mallard and Ringed Plover. Small numbers of Little Tern, a species listed on Annex I of the E.U. Birds Directive, have bred on a few occasions at Portmarnock Point but not since 1991. The area surrounding Baldoyle Bay is densely populated and so the main threats to the site include visitor pressure, disturbance to wildfowl and dumping. In particular, the dumping of spoil onto the foreshore presents a threat to the value of the site. Baldoyle Bay is a fine example of an estuarine system. It contains four habitats listed on Annex I of the E.U. Habitats Directive, and supports two legally protected plant species. The site is also an important bird area and part of it is a Special Protection Area under the E.U. Birds Directive, as well as being a Statutory Nature Reserve. It supports internationally important numbers of Brent Goose and nationally important numbers of six other bird species, including two Annex I Birds Directive species.

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SITE SYNOPSIS

Version date: 12.08.2013 1 of 2 000205_Rev13.Doc

Site Name: Malahide Estuary SAC Site Code: 000205 Malahide Estuary is situated immediately north of Malahide and east of Swords in Co. Dublin. It is the estuary of the River Broadmeadow. The site is divided by a railway viaduct which was built in the 1800s. The site is a Special Area of Conservation (SAC) selected for the following habitats and/or species listed on Annex I / II of the E.U. Habitats Directive (* = priority; numbers in brackets are Natura 2000 codes):

[1140] Tidal Mudflats and Sandflats [1310] Salicornia Mud [1320] Spartina Swards [1330] Atlantic Salt Meadows [1410] Mediterranean Salt Meadows [2120] Marram Dunes (White Dunes) [2130] Fixed Dunes (Grey Dunes)*

The outer part of the estuary is mostly cut off from the sea by a large sand spit, known as ‘the island’. The outer estuary drains almost completely at low tide, exposing sand and mud flats. There is a large bed of Eelgrass (Dwarf Eelgrass, Zostera noltii, and Narrow-leaved Eelgrass, Z. angustifolia) in the north section of the outer estuary, along with Beaked Tasselweed (Ruppia maritima) and extensive mats of green algae (Enteromorpha spp., Ulva lactuca). Common Cord-grass (Spartina anglica) is also widespread in this sheltered part of the estuary. The dune spit has a well developed outer dune ridge dominated by Marram Grass (Ammophila arenaria). The dry areas of the stabilised dunes have a dense covering of Burnet Rose (Rosa pimpinellifolia), Red Fescue (Festuca rubra) and species such as Yellow-wort (Blackstonia perfoliata), Autumn Gentian (Gentianella amarella), Hound's-tongue (Cynoglossum officinale), Carline Thistle (Carlina vulgaris) and Pyramidal Orchid (Anacamptis pyramidalis). Much of the interior of the spit is taken up by a golf course. The inner stony shore has frequent Sea-holly (Eryngium maritimum). Well-developed saltmarshes occur at the tip of the spit. Atlantic salt meadow is the principle type and is characterised by species such as Sea-purslane (Halimoine portulacoides), Sea Aster (Aster tripolium), Thrift (Armeria maritima), Sea Arrowgrass (Triglochin maritima) and Common Saltmarsh-grass (Puccinellia maritima). Elsewhere in the outer estuary, a small area of Mediterranean salt meadow occurs which is characterised by the presence of Sea Rush (Juncus maritimus). Below the salt marshes

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there are good examples of pioneering glasswort (Salicornia spp.) swards and other annual species, typified by S. dolichostachya and Annual Sea-blite (Suaeda maritima). The inner estuary does not drain at low tide apart from the extreme inner part. Here, patches of saltmarsh and salt meadows occur, with Sea Aster, Sea Plantain (Plantago maritima) and Sea Club-rush (Scirpus maritimus). Beaked Tasselweed occurs in one of the channels. The site includes a fine area of rocky shore south-east of Malahide and extending towards Portmarnock. This represents the only continuous section through the fossiliferous Lower Carboniferous rocks in the Dublin Basin, and is the type locality for several species of fossil coral. The estuary is an important wintering bird site and holds an internationally important population of Brent Goose and nationally important populations of a further 15 species. Average maximum counts during the 1995/96-1997/98 period were: Brent Goose 1217; Great Crested Grebe 52; Mute Swan 106; Shelduck 471; Pochard 200; Goldeneye 333; Red-breasted Merganser 116; Oystercatcher 1228; Golden Plover 2123; Grey Plover 190; Redshank 454; Wigeon 50; Teal 78; Ringed Plover 106; Knot 858; Dunlin 1474; Greenshank 38; Pintail 53; Black-tailed Godwit 345; Bar-tailed Godwit 99. The high numbers of diving birds reflects the lagoon-type nature of the inner estuary. The estuary also attracts migrant species such as Ruff, Curlew Sandpiper, Spotted Redshank and Little Stint. Breeding birds of the site include Ringed Plover, Shelduck and Mallard. Up to the 1950s there was a major tern colony at the southern end of the island and the habitat remains suitable for these birds. The inner part of the estuary is heavily used for water sports. A section of the outer estuary has recently been infilled for a marina and housing development. This site is a fine example of an estuarine system with all the main habitats represented. The site is important ornithologically, with a population of Brent Goose of international significance.

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SITE SYNOPSIS

Version date: 12.08.2013 1 of 3 000206_Rev13.Doc

Site Name: North Dublin Bay SAC Site Code: 000206 This site covers the inner part of north Dublin Bay, the seaward boundary extending from the Bull Wall lighthouse across to the Martello Tower at Howth Head. The North Bull Island is the focal point of this site. The site is a Special Area of Conservation (SAC) selected for the following habitats and/or species listed on Annex I / II of the E.U. Habitats Directive (* = priority; numbers in brackets are Natura 2000 codes):

[1140] Tidal Mudflats and Sandflats [1210] Annual Vegetation of Drift Lines [1310] Salicornia Mud [1330] Atlantic Salt Meadows [1410] Mediterranean Salt Meadows [2110] Embryonic Shifting Dunes [2120] Marram Dunes (White Dunes) [2130] Fixed Dunes (Grey Dunes)* [2190] Humid Dune Slacks [1395] Petalwort (Petalophyllum ralfsii)

North Bull Island is a sandy spit which formed after the building of the South Wall and Bull Wall in the 18th and 19th centuries. It now extends for about 5 km in length and is up to 1 km wide in places. A well-developed and dynamic dune system stretches along the seaward side of the island. Various types of dunes occur, from fixed dune grassland to pioneer communities on foredunes. Marram Grass (Ammophila arenaria) is dominant on the outer dune ridges, with Lyme-grass (Leymus arenarius) and Sand Couch (Elymus farctus) on the foredunes. Behind the first dune ridge, plant diversity increases with the appearance of such species as Wild Pansy (Viola tricolor), Kidney Vetch (Anthyllis vulneraria), Common Bird's-foot-trefoil (Lotus corniculatus), Common Restharrow (Ononis repens), Yellow-rattle (Rhinanthus minor) and Pyramidal Orchid (Anacamptis pyramidalis). In these grassy areas and slacks, the scarce Bee Orchid (Ophrys apifera) occurs. About 1 km from the tip of the island, a large dune slack with a rich flora occurs, usually referred to as the 'Alder Marsh' because of the presence of Alder trees (Alnus glutinosa). The water table is very near the surface and is only slightly brackish. Saltmarsh Rush (Juncus maritimus) is the dominant species, with Meadowsweet (Filipendula ulmaria) and Devil's-bit Scabious (Succisa pratensis) being frequent. The orchid flora is notable and includes Marsh Helleborine (Epipactis palustris), Common

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Twayblade (Listera ovata), Autumn Lady's-tresses (Spiranthes spiralis) and Marsh Orchids (Dactylorhiza spp.). Saltmarsh extends along the length of the landward side of the island. The edge of the marsh is marked by an eroding edge which varies from 20 cm to 60 cm high. The marsh can be zoned into different levels according to the vegetation types present. On the lower marsh, Glasswort (Salicornia europaea), Common Saltmarsh-grass (Puccinellia maritima), Annual Sea-blite (Suaeda maritima) and Greater Sea-spurrey (Spergularia media) are the main species. Higher up in the middle marsh Sea Plantain (Plantago maritima), Sea Aster (Aster tripolium), Sea Arrowgrass (Triglochin maritima) and Thrift (Armeria maritima) appear. Above the mark of the normal high tide, species such as Common Scurvygrass (Cochlearia officinalis) and Sea Milkwort (Glaux maritima) are found, while on the extreme upper marsh, the rushes Juncus maritimus and J. gerardi are dominant. Towards the tip of the island, the saltmarsh grades naturally into fixed dune vegetation. The habitat ‘annual vegetation of drift lines’ is found in places, along the length of Dollymount Strand, with species such as Sea Rocket (Cakile maritima), Oraches (Atriplex spp.) and Prickly Saltwort (Salsola kali). The island shelters two intertidal lagoons which are divided by a solid causeway. The sediments of the lagoons are mainly sands with a small and varying mixture of silt and clay. The north lagoon has an area known as the "Salicornia flat", which is dominated by Salicornia dolichostachya, a pioneer glasswort species, and covers about 25 ha. Beaked Tasselweed (Ruppia maritima) occurs in this area, along with some Narrow-leaved Eelgrass (Zostera angustifolia). Dwarf Eelgrass (Z. noltii) also occurs in Sutton Creek. Common Cordgrass (Spartina anglica) occurs in places but its growth is controlled by management. Green algal mats (Enteromorpha spp., Ulva lactuca) cover large areas of the flats during summer. These sediments have a rich macrofauna, with high densities of Lugworms (Arenicola marina) in parts of the north lagoon. Mussels (Mytilus edulis) occur in places, along with bivalves such as Cerastoderma edule, Macoma balthica and Scrobicularia plana. The small gastropod Hydrobia ulvae occurs in high densities in places, while the crustaceans Corophium volutator and Carcinus maenas are common. The sediments on the seaward side of North Bull Island are mostly sands. The site extends below the low spring tide mark to include an area of the sublittoral zone. Three rare plant species which are legally protected under the Flora (Protection) Order, 1999 have been recorded on the North Bull Island. These are Lesser Centaury (Centaurium pulchellum), Red Hemp-nettle (Galeopsis angustifolia) and Meadow Saxifrage (Saxifraga granulata). Two further species listed as threatened in the Red Data Book, Wild Clary/Sage (Salvia verbenaca) and Spring Vetch (Vicia lathyroides), have also been recorded. A rare liverwort, Petalophyllum ralfsii, was first recorded from the North Bull Island in 1874 and has recently been confirmed as still present. This species is of high conservation value as it is listed on Annex II of the E.U. Habitats Directive. The North Bull is the only known extant site for the species in Ireland away from the western seaboard.

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North Dublin Bay is of international importance for waterfowl. During the 1994/95 to 1996/97 period the following species occurred in internationally important numbers (figures are average maxima): Brent Goose 2,333; Knot 4,423; Bar-tailed Godwit 1,586. A further 14 species occurred in nationally important concentrations - Shelduck 1505; Wigeon 1,166; Teal 1,512; Pintail 334; Shoveler 239; Oystercatcher 2,190; Ringed Plover 346; Grey Plover 816; Sanderling 357; Dunlin 6,238; Black-tailed Godwit 156; Curlew 1,193; Turnstone 197 and Redshank 1,175. Some of these species frequent South Dublin Bay and the River Tolka Estuary for feeding and/or roosting purposes (mostly Brent Goose, Oystercatcher, Ringed Plover, Sanderling and Dunlin). The tip of the North Bull Island is a traditional nesting site for Little Tern. A high total of 88 pairs nested in 1987. However, nesting attempts have not been successful since the early 1990s. Ringed Plover, Shelduck, Mallard, Skylark, Meadow Pipit and Stonechat also nest. A well-known population of Irish Hare is resident on the island The invertebrates of the North Bull Island have been studied and the island has been shown to contain at least seven species of regional or national importance in Ireland (from the Orders Diptera, Hymenoptera and Hemiptera). The main land uses of this site are amenity activities and nature conservation. The North Bull Island is the main recreational beach in Co. Dublin and is used throughout the year. Much of the land surface of the island is taken up by two golf courses. Two separate Statutory Nature Reserves cover much of the island east of the Bull Wall and the surrrounding intertidal flats. The site is used regularly for educational purposes. North Bull Island has been designated a Special Protection Area under the E.U. Birds Directive and it is also a statutory Wildfowl Sanctuary, a Ramsar Convention site, a Biogenetic Reserve, a Biosphere Reserve and a Special Area Amenity Order site. This site is an excellent example of a coastal site with all the main habitats represented. The site holds good examples of nine habitats that are listed on Annex I of the E.U. Habitats Directive; one of these is listed with priority status. Several of the wintering bird species have populations of international importance, while some of the invertebrates are of national importance. The site contains a numbers of rare and scarce plants including some which are legally protected. Its proximity to the capital city makes North Dublin Bay an excellent site for educational studies and research.

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SITE SYNOPSIS

Version date: 12.08.2013 1 of 2 000208_Rev13.Doc

Site Name: Rogerstown Estuary SAC Site Code: 000208 Rogerstown Estuary is situated about 2 km north of Donabate in Co. Dublin. It is a relatively small, narrow estuary separated from the sea by a sand and shingle bar. The estuary is divided by a causeway and narrow bridge, built in the 1840s to carry the Dublin-Belfast railway line. The site is a Special Area of Conservation (SAC) selected for the following habitats and/or species listed on Annex I / II of the E.U. Habitats Directive (* = priority; numbers in brackets are Natura 2000 codes):

[1130] Estuaries [1140] Tidal Mudflats and Sandflats [1310] Salicornia Mud [1330] Atlantic Salt Meadows [1410] Mediterranean Salt Meadows [2120] Marram Dunes (White Dunes) [2130] Fixed Dunes (Grey Dunes)*

The estuary drains almost completely at low tide. The intertidal flats of the outer estuary are mainly of sands, with soft muds in the north-west sector and along the southern shore. Associated with these muds are stands of Common Cordgrass (Spartina anglica). Green algae (mainly Enteromorpha spp. and Ulva lactuca) are widespread and form dense mats in the more sheltered areas. The intertidal angiosperm Beaked Tasselweed (Ruppia maritima) grows profusely in places beneath the algal mats. The Lugworm (Arenicola marina) is common in the outer estuary and large Mussel beds (Mytilus edulis) occur at the outlet to the sea. The area of intertidal flats in the inner estuary is reduced as a result of the local authority refuse tip on the north shore. The sediments are mostly muds, which are very soft in places. Common Cordgrass is widespread in parts, and in summer, dense green algal mats grow on the muds. In the extreme inner part, the estuary narrows to a tidal river. The habitat ‘Salicornia mud’ occurs in both the outer and inner estuaries, and S. dolichostachya is the main glasswort species found. Other species include S. ramosissima, S. europaea and Annual Sea-blite (Suaeda maritima). Saltmarsh fringes parts of the estuary, especially the southern shores and parts of the outer sand spit. Common plant species of the saltmarsh include Sea Rush (Juncus

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maritimus), Sea-purslane (Halimione portulacoides) and Common Saltmarsh-grass (Puccinellia maritima). Salt meadows and wet brackish fields occur along the tidal river. Low sand hills occur on the outer spit, including some small areas of fixed dunes and Marram Grass (Ammophila arenaria) dunes. Fine sandy beaches and intertidal sandflats occur at the outer part of the estuary. Two plant species which are legally protected under the Flora (Protection) Order, 1999, occur within the site: Hairy Violet (Viola hirta) occurs on the sand spit and Meadow Barley (Hordeum secalinum) occurs in the saline fields of the inner estuary. This species has declined, apparently due to reclamation and embankment of lands fringing estuaries. Another rare species, Green-winged Orchid (Orchis morio), occurs in the sandy areas of the outer estuary. Rogerstown Estuary is an important waterfowl site, with Brent Goose having a population of international importance (1176). A further 16 species have populations of national importance: Greylag Goose (186), Shelduck (785), Teal (584), Pintail (30), Shoveler (69), Oystercatcher (1028), Ringed Plover (152), Golden Plover (1813), Grey Plover (245), Lapwing (4056), Knot (2076), Dunlin (2625), Sanderling (57), Black-tailed Godwit (272), Curlew (1549), Redshank (732) and Greenshank (22) (All counts are average peaks over four winters 1994/95 - 1997/98). The presence of a significant population of Golden Plover is of note and this species is listed on Annex I of the E.U. Birds Directive. The estuary is a regular staging post for autumn migrants, especially Green Sandpiper, Ruff, Little Stint, Curlew Sandpiper and Spotted Redshank. Little Tern has bred at the outer sand spit, but much of the nesting area has now been washed away as a result of erosion. The maximum number of pairs recorded was 17 in 1991. Ringed Plover breed in the same area. The outer part of the estuary has been designated a Statutory Nature Reserve and a Special Protection Area under the E.U. Birds Directive. The inner estuary has been damaged by the refuse tip which covers 40 ha of mudflat. This site is a good example of an estuarine system, with all typical habitats represented, including several listed on Annex I of the E.U. Habitats Directive. Rogerstown is an internationally important waterfowl site and has been a breeding site for Little Terns. The presence within the site of three rare plant species adds to its importance.

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SITE SYNOPSIS

Version date: 10.12.2015 1 of 2 000210_Rev15.Docx

Site Name: South Dublin Bay SAC Site Code: 000210 This site lies south of the River Liffey in Co. Dublin, and extends from the South Wall to the west pier at Dun Laoghaire. It is an intertidal site with extensive areas of sand and mudflats. The sediments are predominantly sands but grade to sandy muds near the shore at Merrion Gates. The main channel which drains the area is Cockle Lake. The site is a Special Area of Conservation (SAC) selected for the following habitats and/or species listed on Annex I / II of the E.U. Habitats Directive (* = priority; numbers in brackets are Natura 2000 codes):

[1140] Tidal Mudflats and Sandflats [1210] Annual vegetation of drift lines [1310] Salicornia and other annuals colonising mud and sand [2110] Embryonic shifting dunes

The bed of Dward Eelgrass (Zostera noltii) found below Merrion Gates is the largest stand on the east coast. Green algae (Enteromorpha spp. and Ulva lactuca) are distributed throughout the area at a low density. Fucoid algae occur on the rocky shore in the Maretimo to Dún Laoghaire area. Species include Fucus spiralis, F. vesiculosus, F. serratus, Ascophyllum nodosum and Pelvetia canaliculata. Several small, sandy beaches with incipient dune formation occur in the northern and western sectors of the site, notably at Poolbeg, Irishtown and Merrion/ Booterstown. The formation at Booterstown is very recent. Drift line vegetation occurs in association with the embryonic and incipient fore dunes. Typically drift lines occur in a band approximately 5 m wide, though at Booterstown this zone is wider in places. The habitat occurs just above the High Water Mark and below the area of embryonic dune. Species present are Sea Rocket (Cakile maritima), Frosted Orache (Atriplex laciniata), Spear-leaved Orache (A. prostrata), Prickly Saltwort (Salsola kali) and Fat Hen (Chenopodium album). Also occurring is Sea Sandwort (Honkenya peploides), Sea Beet (Beta vulgaris subsp. maritima) and Annual Sea-blite (Suaeda maritima). A small area of pioneer saltmarsh now occurs in the lee of an embryonic sand dune just north of Booterstown Station. This early stage of saltmarsh development is here characterised by the presence of pioneer stands of glassworts (Salicornia spp.) occurring below an area of drift line vegetation. As this is of very recent origin, it covers a small area but ample areas of substrate and shelter are available for the further development of this habitat.

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Lugworm (Arenicola marina), Cockles (Cerastoderma edule) and annelids and other bivalves are frequent throughout the site. The small gastropod Hydrobia ulvae occurs on the muddy sands off Merrion Gates. South Dublin Bay is an important site for waterfowl. Although birds regularly commute between the south bay and the north bay, recent studies have shown that certain populations which occur in the south bay spend most of their time there. The principal species are Oystercatcher (1215), Ringed Plover (120), Sanderling (344), Dunlin (2628) and Redshank (356) (average winter peaks 1996/97 and 1997/98). Up to 100 Turnstones are usual in the south bay during winter. Brent Goose regularly occur in numbers of international importance (average peak 299). Bar-tailed Godwit (565), a species listed on Annex I of the E.U. Birds Directive, also occur. Large numbers of gulls roost in South Dublin Bay, e.g. 4,500 Black-headed Gulls in February 1990; 500 Common Gulls in February 1991. It is also an important tern roost in the autumn, regularly holding 2000-3000 terns including Roseate Terns, a species listed on Annex I of the E.U. Birds Directive. South Dublin Bay is largely protected as a Special Protection Area. At low tide the inner parts of the south bay are used for amenity purposes. Bait-digging is a regular activity on the sandy flats. At high tide some areas have wind-surfing and jet-skiing. This site is a fine example of a coastal system, with extensive sand and mudflats, and incipient dune formations. South Dublin Bay is also an internationally important bird site.

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SITE SYNOPSIS

Version date: 11.10.2013 1 of 2 001398_Rev13.Doc

Site Name: Rye Water Valley/Carton SAC Site Code: 001398 Rye Water Valley/Carton SAC is located between Leixlip and Maynooth, in Counties Meath and Kildare, and extends along the Rye Water, a tributary of the River Liffey. The site is a Special Area of Conservation (SAC) selected for the following habitats and/or species listed on Annex I / II of the E.U. Habitats Directive (* = priority; numbers in brackets are Natura 2000 codes):

[7220] Petrifying Springs* [1014] Narrow-mouthed Whorl Snail (Vertigo angustior) [1016] Desmoulin's Whorl Snail (Vertigo moulinsiana)

The Rye Water in Carton Estate is dammed at intervals, creating a series of lakes. Reed Sweet-grass (Glyceria maxima) is frequent around the lakes, along with Yellow Iris (Iris pseudacorus), Reed Canary-grass (Phalaris arundinacea), Bulrush (Typha latifolia), Water Forget-me-not (Myosotis scorpioides), Marsh-marigold (Caltha palustris) and starworts (Callitriche spp.). Along the remainder of the site the river has been dredged and much of the reed fringe removed. To the north-west of Carton Bridge a small clump of willows (Salix spp.), with dogwood (Cornus sp.), Alder (Alnus glutinosa), Ash (Fraxinus excelsior) and Elder (Sambucus nigra) occurs. The ground flora found here includes Golden Saxifrage (Chrysosplenium oppostifolium), Meadowsweet (Filipendula ulmaria), Common Valerian (Valeriana officinalis), Wavy Bitter-cress (Cardamine flexuosa) and Bittersweet (Solanum dulcamara). The woods on Carton Estate are mostly old demesne woods with both deciduous and coniferous species. Conifers, including some Yew (Taxus baccata) – a native species, are dominant, with Beech (Fagus sylvatica), oak (Quercus sp.), Sycamore (Acer pseudoplatanus), Ash and Hazel (Corylus avellana) also occurring. The ground flora is dominated by Ivy (Hedera helix), with such species as Hedge Woundwort (Stachys sylvatica), Wood Speedwell (Veronica montana), Woodruff (Galium odoratum), Wood Avens (Geum urbanum), Common Dog-violet (Viola riviniana), Wild Angelica (Angelica sylvestris), Ramsons (Allium ursinum), Ground-ivy (Glechoma hederacea) and Ivy Broomrape (Orobanche hederae) also found. Hairy St. John's-wort (Hypericum hirsutum), a species legally protected under the Flora (Protection) Order, 1999, occurs in Carton Estate and there is an old record from the estate for the similarly protected Hairy Violet (Viola hirta). However, this latter species has not been recorded from the site in recent years. Another species

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listed in the Red Data Book, Green Figwort (Scrophularia umbrosa), occurs on the site in several locations by the Rye Water. The woods at Carton Demesne are the site of a rare Myxomycete fungus, Diderma deplanatum. The marsh, mineral spring and seepage area found at Louisa Bridge supports a good diversity of plant species, including stoneworts, Marsh Arrowgrass (Triglochin palustris), Purple Moor-grass (Molinea caerulea), sedges (Carex spp.), Common Butterwort (Pinguicula vulgaris), Marsh Lousewort (Pedicularis palustris), Grass-of-parnassus (Parnassia palustris) and Cuckooflower (Cardamine pratensis). The mineral spring found at the site is of a type considered to be rare in Europe and is a habitat listed on Annex I of the E.U. Habitats Directive. The Red Data Book species Blue Fleabane (Erigeron acer) is found growing on a wall at Louisa Bridge. Within the woods, Blackcap, Woodcock and Long-eared Owl have been recorded. Little Grebe, Coot, Moorhen, Tufted Duck, Teal and Kingfisher, the latter a species listed on Annex I of the E.U. Birds Directive, occur on and about the lake. The Rye Water is also a spawning ground for Trout and Salmon, and the rare, White-clawed Crayfish (Austropotamobius pallipes) has been recorded at Leixlip. The latter two species are listed on Annex II of the E.U. Habitats Directive. The rare Narrow-mouthed Whorl Snail and Desmoulin’s Whorl Snail occur in marsh vegetation near Louisa Bridge. Both are rare in Ireland and in Europe, and are listed on Annex II of the E.U. Habitats Directive. The scarce dragonfly, Orthetrum coerulescens, has also been recorded at Louisa Bridge. The conservation importance of the site lies in the presence of several rare and threatened plant and animal species, and the presence of petrifying springs, a habitat type listed on Annex I of the E.U. Habitats Directive. The woods found on Carton Estate and their birdlife are of additional interest.

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SITE SYNOPSIS SITE NAME: NORTH BULL ISLAND SPA SITE CODE: 004006 This site covers all of the inner part of north Dublin Bay, with the seaward boundary extending from the Bull Wall lighthouse across to Drumleck Point at Howth Head. The North Bull Island sand spit is a relatively recent depositional feature, formed as a result of improvements to Dublin Port during the 18th and 19th centuries. It is almost 5 km long and 1 km wide and runs parallel to the coast between Clontarf and Sutton. Part of the interior of the island has been converted to golf courses. Saltmarsh extends along the length of the landward side of the island and provides the main roost site for wintering birds in Dublin Bay. The island shelters two intertidal lagoons which are divided by a solid causeway. These lagoons provide the main feeding grounds for the wintering waterfowl. The sediments of the lagoons are mainly sands with a small and varying mixture of silt and clay. Green algal mats (Ulva spp.) are a feature of the flats during summer. These sediments have a rich macro-invertebrate fauna, with high densities of Lugworm (Arenicola marina) and Ragworm (Hediste diversicolor). The site is a Special Protection Area (SPA) under the E.U. Birds Directive, of special conservation interest for the following species: Light-bellied Brent Goose, Shelduck, Teal, Pintail, Shoveler, Oystercatcher, Golden Plover, Grey Plover, Knot, Sanderling, Dunlin, Black-tailed Godwit, Bar-tailed Godwit, Curlew, Redshank, Turnstone and Black-headed Gull. The site is also of special conservation interest for holding an assemblage of over 20,000 wintering waterbirds. The E.U. Birds Directive pays particular attention to wetlands and, as these form part of this SPA, the site and its associated waterbirds are of special conservation interest for Wetland & Waterbirds. The North Bull Island SPA is of international importance for waterfowl on the basis that it regularly supports in excess of 20,000 waterfowl. The site supports internationally important populations of three species, Light-bellied Brent Goose (1,548), Black-tailed Godwit (367) and Bar-tailed Godwit (1,529) - all figures are mean peaks for the five winters between 1995/96 and 1999/2000. The site is one of the most important in the country for Light-bellied Brent Goose. A further 14 species have populations of national importance – Shelduck (1,259), Teal (953), Pintail (233), Shoveler (141), Oystercatcher (1,784), Grey Plover (517), Golden Plover (2,033), Knot (2,837), Sanderling (141), Dunlin (4,146), Curlew (937), Redshank (1,431), Turnstone (157) and Black-headed Gull (2,196). The populations of Pintail and Knot are of particular note as they comprise 14% and 10% respectively of the all-Ireland population totals. Other species that occur regularly in winter include Grey Heron, Little Egret, Cormorant, Wigeon, Goldeneye, Red-breasted Merganser, Ringed Plover and Greenshank. Gulls are a feature of the site during winter and, along with the nationally important population of Black-headed Gull (2,196), other species that occur include Common Gull (332) and Herring Gull (331). While some of the birds

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also frequent South Dublin Bay and the River Tolka Estuary for feeding and/or roosting purposes, the majority remain within the site for much of the winter. The wintering bird populations have been monitored more or less continuously since the late 1960s and the site is now surveyed each winter as part of the larger Dublin Bay complex. The North Bull Island SPA is a regular site for passage waders, especially Ruff, Curlew Sandpiper and Spotted Redshank. These are mostly observed in single figures in autumn but occasionally in spring or winter. The site formerly had an important colony of Little Tern but breeding has not occurred in recent years. Several pairs of Ringed Plover breed, along with Shelduck in some years. Breeding passerines include Skylark, Meadow Pipit, Stonechat and Reed Bunting. The island is a regular wintering site for Short-eared Owl, with up to 5 present in some winters. The North Bull Island SPA is an excellent example of an estuarine complex and is one of the top sites in Ireland for wintering waterfowl. It is of international importance on account of both the total number of waterfowl and the individual populations of Light-bellied Brent Goose, Black-tailed Godwit and Bar-tailed Godwit that use it. Also of significance is the regular presence of several species that are listed on Annex I of the E.U. Birds Directive, notably Golden Plover and Bar-tailed Godwit, but also Ruff and Short-eared Owl. North Bull Island is a Ramsar Convention site, and part of the North Bull Island SPA is a Statutory Nature Reserve and a Wildfowl Sanctuary.

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25.3.2014

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SITE SYNOPSIS SITE NAME: ROGERSTOWN ESTUARY SPA SITE CODE: 004015 Rogerstown Estuary is situated about 2 km north of Donabate in north County Dublin. It is a relatively small, funnel shaped estuary separated from the sea by a sand and shingle peninsula; the site extends eastwards to include an area of shallow marine water. The estuary receives the waters of the Ballyboghil and Ballough rivers and has a wide salinity range, from near full seawater to near full freshwater. The estuary is divided by a causeway and narrow bridge, built in the 1840s to carry the Dublin-Belfast railway line. At low tide extensive intertidal sand and mud flats are exposed and these provide the main food resource for the wintering waterfowl that use the site. The intertidal flats of the estuary are mainly of sands, with soft muds in the north-west sector and along the southern shore. Associated with these muds are stands of Common Cord-grass (Spartina anglica). Green algae (mainly Ulva spp.) are widespread and form dense mats in the more sheltered areas. The intertidal vascular plant Beaked Tasselweed (Ruppia maritima) grows profusely in places beneath the algal mats and is grazed by herbivorous waterfowl (notably Light-bellied Brent Goose and Wigeon). Salt marsh fringes parts of the estuary, especially its southern shores. Common plant species of the saltmarsh include Sea Rush (Juncus maritimus), Sea Purslane (Halimione portulacoides) and Common Saltmarsh-grass (Puccinellia maritima). The site is a Special Protection Area (SPA) under the E.U. Birds Directive, of special conservation interest for the following species: Greylag Goose, Light-bellied Brent Goose, Shelduck, Shoveler, Oystercatcher, Ringed Plover, Grey Plover, Knot, Dunlin, Black-tailed Godwit and Redshank. The E.U. Birds Directive pays particular attention to wetlands and, as these form part of this SPA, the site and its associated waterbirds are of special conservation interest for Wetland & Waterbirds. Rogerstown Estuary is an important winter waterfowl site and supports a population of Light-bellied Brent Goose of international importance (1,069) - all counts are mean peaks over the five winters 1995/96 – 1999/2000. A further 10 species have populations of national importance as follows: Greylag Goose (160), Shelduck (773), Shoveler (59), Oystercatcher (1,345), Ringed Plover (188), Grey Plover (229), Knot (2,454), Dunlin (2,745), Black-tailed Godwit (195) and Redshank (490). The Greylag Geese are part of a larger population which spends most of the winter on Lambay Island. Other species which occur regularly include Wigeon (358), Teal (346), Mallard (214), Red-breasted Merganser (30), Golden Plover (1,059) Lapwing (2,129), Sanderling (50), Curlew (505) and Turnstone (77). Large numbers of gulls including Herring Gull, Great Black-backed Gull and Black-headed Gull are attracted to the area, partly due to the presence of an adjacent local authority landfill site. Little Egret, a species which has recently colonised Ireland, also occurs at this site.

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Some of the wader species also occur on passage, notably Black-tailed Godwit with numbers often exceeding 300 in April. The estuary is a regular staging post for scarce migrants, especially in autumn when Green Sandpiper, Ruff, Little Stint, Curlew Sandpiper and Spotted Redshank may be seen. Shelduck breed within the site. Rogerstown Estuary SPA is an important link in the chain of estuaries on the east coast. It supports an internationally important population of Light-bellied Brent Goose and nationally important populations of a further 10 species. The presence of Little Egret and Golden Plover is of note as these species are listed on Annex I of the E.U. Birds Directive. Rogerstown Estuary is also a Ramsar Convention site, and part of Rogerstown Estuary SPA is designated as a Statutory Nature Reserve and a Wildfowl Sanctuary. 25.3.2014

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SITE SYNOPSIS SITE NAME: BALDOYLE BAY SPA SITE CODE: 004016 Baldoyle Bay, located to the north and east of Baldoyle and to the south of Portmarnock, Co. Dublin, is a relatively small, narrow estuary separated from the open sea by a large sand dune system. Two small rivers, the Mayne River and the Sluice River, flow into the inner part of the estuary. Large areas of intertidal flats are exposed at low tide. These are mostly sands but grade to muds in the inner sheltered parts of the estuary. Extensive areas of Common Cord-grass (Spartina anglica) occur in the inner estuary. Both the Narrow-leaved Eelgrass (Zostera angustifolia) and the Dwarf Eelgrass (Z. noltii) are also found here. During summer, the sandflats of the sheltered areas are covered by mats of green algae (Ulva spp.). The sediments have a typical macrofauna, with Lugworm (Arenicola marina) dominating the sandy flats. Areas of saltmarsh occur near Portmarnock Bridge and at Portmarnock Point, with narrow strips found along other parts of the estuary. Species such as Glasswort (Salicornia spp.), Sea-purslane (Halimione portulacoides), Sea Plantain (Plantago maritima) and Sea Rush (Juncus maritimus) are found here. The site is a Special Protection Area (SPA) under the E.U. Birds Directive, of special conservation interest for the following species: Light-bellied Brent Goose, Shelduck, Ringed Plover, Golden Plover, Grey Plover and Bar-tailed Godwit. The E.U. Birds Directive pays particular attention to wetlands and, as these form part of this SPA, the site and its associated waterbirds are of special conservation interest for Wetland & Waterbirds. Baldoyle Bay is an important site for wintering waterfowl, providing good quality feeding areas and roost sites for an excellent diversity of waterfowl species. It supports an internationally important population of Light-bellied Brent Goose (726), and has a further five species with nationally important populations (all figures are mean peaks for the five winters 1995/96 to 1999/2000): Shelduck (147), Ringed Plover (223), Golden Plover (2,120), Grey Plover (200) and Bar-tailed Godwit (353). Other species which occur include Great Crested Grebe (42), Pintail (35), Teal (138), Mallard (46), Common Scoter (61), Oystercatcher (531), Lapwing (524), Knot (189), Dunlin (879), Black-tailed Godwit (113), Curlew (98), Redshank (224), Greenshank (11) and Turnstone (43). Regular breeding birds include Shelduck, Mallard and Ringed Plover. In autumn, passage migrants such as Curlew Sandpiper, Spotted Redshank and Green Sandpiper are regular in small numbers. Little Egret, a species which has recently colonised Ireland, also occurs at this site.

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Baldoyle Bay SPA is of high conservation importance, for supporting internationally important numbers of Light-bellied Brent Goose as well as nationally important populations of a further five species, including Golden Plover and Bar-tailed Godwit, both species that are listed on Annex I of the E.U. Birds Directive. The inner part of the site is a Statutory Nature Reserve and also designated as a wetland of international importance under the Ramsar Convention.

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SITE SYNOPSIS SITE NAME: SOUTH DUBLIN BAY AND RIVER TOLKA ESTUARY SPA SITE CODE: 004024 The South Dublin Bay and River Tolka Estuary SPA comprises a substantial part of Dublin Bay. It includes the intertidal area between the River Liffey and Dun Laoghaire, and the estuary of the River Tolka to the north of the River Liffey, as well as Booterstown Marsh. A portion of the shallow marine waters of the bay is also included. In the south bay, the intertidal flats extend for almost 3 km at their widest. The sediments are predominantly well-aerated sands. Several permanent channels exist, the largest being Cockle Lake. A small sandy beach occurs at Merrion Gates, while some bedrock shore occurs near Dun Laoghaire. The landward boundary is now almost entirely artificially embanked. There is a bed of Dwarf Eelgrass (Zostera noltii) below Merrion Gates which is the largest stand on the east coast. Green algae (Ulva spp.) are distributed throughout the area at a low density. The macro-invertebrate fauna is well-developed, and is characterised by annelids such as Lugworm (Arenicola marina), Nephthys spp. and Sand Mason (Lanice conchilega), and bivalves, especially Cockle (Cerastoderma edule) and Baltic Tellin (Macoma balthica). The small gastropod Spire Shell (Hydrobia ulvae) occurs on the muddy sands off Merrion Gates, along with the crustacean Corophium volutator. Sediments in the Tolka Estuary vary from soft thixotrophic muds with a high organic content in the inner estuary to exposed, well-aerated sands off the Bull Wall. The site includes Booterstown Marsh, an enclosed area of saltmarsh and muds that is cut off from the sea by the Dublin/Wexford railway line, being linked only by a channel to the east, the Nutley stream. Sea water incursions into the marsh occur along this stream at high tide. An area of grassland at Poolbeg, north of Irishtown Nature Park, is also included in the site. The site is a Special Protection Area (SPA) under the E.U. Birds Directive, of special conservation interest for the following species: Light-bellied Brent Goose, Oystercatcher, Ringed Plover, Grey Plover, Knot, Sanderling, Dunlin, Bar-tailed Godwit, Redshank, Black-headed Gull, Roseate Tern, Common Tern and Arctic Tern. The E.U. Birds Directive pays particular attention to wetlands, and as these form part of the SPA, the site and its associated waterbirds are of special conservation interest for Wetland & Waterbirds. The site is an important site for wintering waterfowl, being an integral part of the internationally important Dublin Bay complex – all counts for wintering waterbirds are five year mean peaks for the period 1995/96 to 1999/2000. Although birds regularly commute between the south bay and the north bay, recent studies have shown that certain populations which occur in the south bay spend most of their time there. An internationally important population of Light-bellied Brent Goose (368) occurs regularly and newly arrived birds in the autumn feed on the Eelgrass bed at

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Merrion. At the time of designation the site supported nationally important numbers of a further nine species: Oystercatcher (1,145), Ringed Plover (161), Grey Plover (45), Knot (548), Sanderling (321), Dunlin (1,923), Bar-tailed Godwit (766), Redshank (260) and Black-headed Gull (3,040). Other species occurring in smaller numbers include Great Crested Grebe (21), Curlew (127) and Turnstone (52). Little Egret, a species which has recently colonised Ireland, also occurs at this site. South Dublin Bay is a significant site for wintering gulls, with a nationally important population of Black-headed Gull, but also Common Gull (330) and Herring Gull (348). Mediterranean Gull is also recorded from here, occurring through much of the year, but especially in late winter/spring and again in late summer into winter. Both Common Tern and Arctic Tern breed in Dublin Docks, on a man-made mooring structure known as the E.S.B. dolphin – this is included within the site. Small numbers of Common Tern and Arctic Tern were recorded nesting on this dolphin in the 1980s. A survey in 1995 recorded nationally important numbers of Common Tern nesting here (52 pairs). The breeding population of Common Tern at this site has increased, with 216 pairs recorded in 2000. This increase was largely due to the ongoing management of the site for breeding terns. More recent data highlights this site as one of the most important Common Tern sites in the country with over 400 pairs recorded here in 2007. South Dublin Bay is an important staging/passage site for a number of tern species in the autumn (mostly late July to September). The origin of many of the birds is likely to be the Dublin breeding sites (Rockabill and the Dublin Docks) though numbers suggest that the site is also used by birds from other sites, perhaps outside the state. This site is selected for designation for its autumn tern populations: Roseate Tern (2,000 in 1999), Common Tern (5,000 in 1999) and Arctic Tern (20,000 in 1996). The South Dublin Bay and River Tolka Estuary SPA is of ornithological importance as it supports an internationally important population of Light-bellied Brent Goose and nationally important populations of a further nine wintering species. Furthermore, the site supports a nationally important colony of breeding Common Tern and is an internationally important passage/staging site for three tern species. It is of note that four of the species that regularly occur at this site are listed on Annex I of the E.U. Birds Directive, i.e. Bar-tailed Godwit, Common Tern, Arctic Tern and Roseate Tern. Sandymount Strand/Tolka Estuary is also a Ramsar Convention site.

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30.5.2015

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SITE SYNOPSIS SITE NAME: MALAHIDE ESTUARY SPA SITE CODE: 004025 Malahide Estuary is situated in north Co. Dublin, between the towns of Malahide and Swords. The site encompasses the estuary, saltmarsh habitats and shallow subtidal areas at the mouth of the estuary. A railway viaduct, built in the 1800s, crosses the site and has led to the inner estuary becoming lagoonal in character and only partly tidal. Much of the outer part of the estuary is well-sheltered from the sea by a large sand spit, known as “The Island”. This spit is now mostly converted to golf-course. The outer part empties almost completely at low tide and there are extensive intertidal flats exposed. Substantial stands of eelgrass (both Zostera noltii and Z. angustifolia) occur in the sheltered part of the outer estuary, along with Tasselweed (Ruppia maritima). Green algae, mostly Ulva spp., are frequent on the sheltered flats. Common Cord-grass (Spartina anglica) is well established in the outer estuary and also in the innermost part of the site. The intertidal flats support a typical macro-invertebrate fauna, with polychaete worms (Arenicola marina and Hediste diversicolor), bivalves such as Cerastoderma edule, Macoma balthica and Scrobicularia plana, the small gastropod Hydrobia ulvae and the crustacean Corophium volutator. Salt marshes, which provide important roosts during high tide, occur in parts of the outer estuary and in the extreme inner part of the inner estuary. These are characterised by such species as Sea Purslane (Halimione portulacoides), Sea Aster (Aster tripolium), Thrift (Armeria maritima), Sea Arrowgrass (Triglochin maritima) and Common Saltmarsh-grass (Puccinellia maritima). The site is a Special Protection Area (SPA) under the E.U. Birds Directive, of special conservation interest for the following species: Great Crested Grebe, Light-bellied Brent Goose, Shelduck, Pintail, Goldeneye, Red-breasted Merganser, Oystercatcher, Golden Plover, Grey Plover, Knot, Dunlin, Black-tailed Godwit, Bar-tailed Godwit and Redshank. The E.U. Birds Directive pays particular attention to wetlands and, as these form part of this SPA, the site and its associated waterbirds are of special conservation interest for Wetland & Waterbirds. This site is of high importance for wintering waterfowl and supports a particularly good diversity of species. It has internationally important populations of Light-bellied Brent Goose (1,104 individuals or 5% of the all-Ireland total) and Black-tailed Godwit (409 individuals or 2.9% of the all-Ireland total) - figures given here and below are mean peaks for the five winters 1995/96-1999/2000. Furthermore, the site supports nationally important populations of an additional 12 species: Great Crested Grebe (63), Shelduck (439), Pintail (58), Goldeneye (215), Red-breasted Merganser (99), Oystercatcher (1,360), Golden Plover (1,843), Grey Plover (201), Knot (915), Dunlin (1,594), Bar-tailed Godwit (156) and Redshank (581). The high numbers of diving ducks reflects the lagoon-type nature of the inner estuary, and this is one of the few sites in eastern Ireland where substantial numbers of Goldeneye can be found.

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A range of other species occurs, including Mute Swan (37), Pochard (36), Ringed Plover (86), Lapwing (1,542), Curlew (548), Greenshank (38) and Turnstone (112). The estuary also attracts other migrant wader species such as Ruff, Curlew Sandpiper, Spotted Redshank and Little Stint. These occur mainly in autumn, though occasionally in spring and winter. Breeding birds of the site include Ringed Plover, Shelduck and Mallard. Up to the 1950s there was a major tern colony at the southern end of Malahide Island. Grey Herons breed nearby and feed regularly within the site. Malahide Estuary SPA is a fine example of an estuarine system, providing both feeding and roosting areas for a range of wintering waterfowl. The lagoonal nature of the inner estuary is of particular value as it increases the diversity of birds which occur. The site is of high conservation importance, with internationally important populations of Light-bellied Brent Goose and Black-tailed Godwit, and nationally important populations of a further 12 species. Two of the species which occur regularly (Golden Plover and Bar-tailed Godwit) are listed on Annex I of the E.U. Birds Directive. Malahide Estuary (also known as Broadmeadow Estuary) is a Ramsar Convention site.

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23.8.2013

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