roseate tern nesting

Tj -18 -15 TD 0.014 Tc (Andre) Tj -0.5911 Tc (w) Tj 0.0188 Tc 0.2392 Tw (, J. �� Tj -42 -17.04 TD /F4 11.04 Tf -0.0173 Tc (H2.2) Tj 8.64 Tc (.) << 0000206194 00000 n >> 284 State Street �� Croxall, ) Tj -1.0978 Tc 0 Tw (P) Tj 0.0087 Tc 0.2613 Tw (.G.H. Tj -0.8056 Tc 0 Tw (T) Tj 0.0168 Tc 0.5368 Tw (. /ProcSet 2 0 R Continuing thi) Tj 7.7054 Tc 0 Tw (s) Tj 0 -13.08 TD -0.0195 Tc -0.3841 Tw (management action may eventually restore Bush Key as a safe alternate nestin) Tj 6.48 Tc 0 Tw (g) Tj 0 -12.96 TD -0.0218 Tc 0.3418 Tw (site for roseate terns) Tj 9.24 Tc 0 Tw (.) Biological Conservation 25:103-125) Tj 8.31 Tc 0 Tw (.) /Type /XObject /Parent 40 0 R Other important factors include absence of predators an) Tj 6.48 Tc 0 Tw (d) Tj T* -0.0214 Tc 0.2914 Tw (minimal amounts of human disturbance) Tj 9.24 Tc 0 Tw (.) Tj 18 -12.96 TD 0.0014 Tc 0.2686 Tw (U.S. /Length 35 0 R � << 0+21�\V�8V\\��cV8V8�]��22��8�2122�\��8V9�\�c��߇�౲��\��Ӹ��Ա��ٱ౱��Ը�ᱲ�Ჱ��ԷԱ��ٱ��ⱱ��c�]�d��ߪ౱��Ӳ��્��᱇��ӫ��᫱��ଇ��᳈��ⲉለ�]3^^�� 쳹Ꮘ�^��^��^��d�d�^e��d��^^�^�d�9^^d^�d^d]] Immature bird) Tj 7.7054 Tc 0 Tw (s) Tj ET 60.12 48.72 75.96 0.48 re f BT 0.9955 0 0 0.9955 60.12 34.68 Tm /F1 10 Tf -0.0887 Tc (Pag) Tj 4.4429 Tc (e) Tj 47.1341 0 TD 0.0281 Tc (4-43) Tj 4.4429 Tc (4) Tj ET BT 1 0 0 1 60.12 728.64 Tm /F1 9 Tf 0.4037 Tc (ROSE) Tj 0.3202 Tc -0.542 Tw (ATE TER) Tj 2.5017 Tc 0 Tw (N) Tj 268.1427 0 TD 0.4422 Tc 0.2478 Tw (Multi-Species Recovery Plan for South Florid) Tj 3.9954 Tc 0 Tw (a) Tj ET 59.16 745.68 486 0.48 re f 59.16 717.6 486 0.48 re f endstream /Length 68 0 R The fact that three out of the fiv) Tj 7.0982 Tc 0 Tw (e) Tj 0 -13.08 TD -0.0162 Tc 0.4722 Tw (recoveries are from Guyana, where many of the northeastern birds apparentl) Tj 6.48 Tc 0 Tw (y) Tj 0 -12.96 TD -0.0219 Tc 0.3699 Tw (winter, is consistent with his suggestion. ]?c]ccc�c�c�c߁߇�߇��߇��߇��cV��11 111��0 Tj 0 -16.92 TD /F4 11.04 Tf -0.0046 Tc (S6.1) Tj 8.64 Tc (.) 1992. 11 �11U [\��ᲈ��ૈ��\��[�U2U1[+7 11�V�V\\�]��Ⲳ��^��^��^��^�^�d�e��ሉ��ለ��d�d��d��d��^]�:]22+� stream �� These observation) Tj 7.7054 Tc 0 Tw (s) Tj -39.36 -12.96 TD -0.0177 Tc 0.9862 Tw (suggest that at least some roseate terns remain in the vicinity of the coast o) Tj 8.3237 Tc 0 Tw (f) Tj 0 -12.96 TD -0.0166 Tc 0.2737 Tw (Puerto Rico, rather than traveling to South America) Tj 9.24 Tc 0 Tw (.) The Department also offers technical assistance to property owners who wish to manage their lands to enhance habitat for wildlife. Tj -324 -12.96 TD -0.1759 Tc (dougalli) Tj 9.7709 Tc (i) Tj 38.28 0 TD /F0 11.04 Tf -0.24 Tc 9.48 Tw (, ) Tj 9.24 0 TD /F2 11.04 Tf -0.1838 Tc 4.1438 Tw (S. d. bangs) Tj 9.7709 Tc 0 Tw (i) Tj 64.32 0 TD /F0 11.04 Tf -0.1745 Tc 4.0865 Tw (\(Malayan peninsula eastward including China, th) Tj 7.0982 Tc 0 Tw (e) Tj -111.84 -13.08 TD -0.1809 Tc 1.4476 Tw (Phillipines, Molluccas, Straits of Malacca, New Guinea, Solomon Islands, an) Tj 6.48 Tc 0 Tw (d) Tj 0 -12.96 TD -0.1834 Tc 2.5834 Tw (New Caledonia\),) Tj 0 Tc 9.24 Tw ( ) Tj 79.92 0 TD /F2 11.04 Tf -0.1838 Tc 2.6438 Tw (S. d. koruste) Tj 8.5454 Tc 0 Tw (s) Tj 66.84 0 TD /F0 11.04 Tf -0.1807 Tc 2.6207 Tw (\(India and Ceylon eastward to the Malaya) Tj 6.48 Tc 0 Tw (n) Tj -146.76 -12.96 TD -0.1775 Tc 9.4175 Tw (peninsula\), ) Tj 52.2 0 TD /F2 11.04 Tf -0.1793 Tc 2.8193 Tw (S. d. arideensi) Tj 8.5454 Tc 0 Tw (s) Tj 75.72 0 TD /F0 11.04 Tf -0.1817 Tc 2.8217 Tw (\(Seychelles and Madagascar\), and) Tj 0 Tc 9.24 Tw ( ) Tj 158.88 0 TD /F2 11.04 Tf -0.1785 Tc 2.8785 Tw (S. d. gracili) Tj 8.5454 Tc 0 Tw (s) Tj -286.8 -13.08 TD /F0 11.04 Tf -0.1805 Tc (\(Australia\)) Tj 9.24 Tc (.) 1998. endobj /F1 9 0 R /Length 29 0 R endobj Migration and winter quarters of North American roseate terns a) Tj 6.9256 Tc 0 Tw (s) Tj 18 -12.96 TD 0.0167 Tc 0.2533 Tw (shown by banding recoveries. Tj 0 -13.08 TD -0.0176 Tc 0.4699 Tw (Roseate terns tend to be late nesters for terns; nest initiation usually occurs i) Tj 6.48 Tc 0 Tw (n) Tj 0 -12.96 TD -0.0168 Tc -0.0032 Tw (the latter part of May or early June \(Robertson 1978\). The following factors are considered by MDIFW when evaluating a project proposal at roseate tern nesting areas: YES - roseate terns are very sensitive to disturbance during their nesting season. Tj ET 198.12 371.28 345.96 0.48 re f BT 0.9995 0 0 0.9995 198.12 357.24 Tm /F1 12 Tf -0.1977 Tc (Taxonom) Tj 5.3305 Tc (y) Tj ET BT 198.12 338.28 TD /F0 11.04 Tf -0.1815 Tc -0.0225 Tw (This species is in the order Charadriiformes, family Laridae, subfamily Sterninae) Tj 9.24 Tc 0 Tw (.) >> @k�d�]�\��]�]�\\V�V�2\V\]\�c��]�V]2�22��0��1 1[U��ӱ��ⲏ��ሲ��଎��߫��߇��߫��߇��\\z[�V[�U�U��[VU7z[�\�[\��ހ߀�߇^�^�]�^�^��d��d��d��d��d��c��߇c��c�߇c��ߌ��^��^��d�@jq�j��]@Ek�j�]��]�]�]�]�\V�V\V9�]ށ��W\]2211+0�0� 1U[[��Ӱ��ᲈᬎ��଎��ᬎ��ૈ��߇��߇��߫��\��܀U�[V7U�U[V[V[��[�\��^�^�^�^��d�^��d��d��]��d��ለ��߇�c��c��߇��^��^��d�?Gj�j��]c@Fk�d��]�߁]�\]�]V\\]V�]ށ��]]]V�V212�1��1�0�01UU[[��౰ӱ��ᲈ�Ჳ�ᬎ��ᇬ��߫��߇��\��U�[V[V[�V[V[\�\��ހ߆^�]�^�^��^�^��d�d��c��d��c��c�cᇎ߇��ߍ��્��౪��ૈ��c��]��d^Fkjk�߇9FdF��c��]�\]\z\]��]��]]\W�22��1�0� 1 �[��ӱ��ӱ��߇��Წ��ᬇ��ଈ�ૈ��߇��\\�[V\[\y��U��[�\�[��d�d��^�^��d��d�d��d��^��d��ለ��d��^c@jG�d��d?jk��c��]��]�\�]�]�c��c{9\V2�21��0�1 U[U��Ӱ��߇��ଲ��⬎�Ꭼ��ᇬ��ᇁ��߀��ހ\\��V�[\z[\[�\�\��\��^�^��c�d��^��d�^��d��d��d��d�d�^��ለ��፫�ᱍ��౱��ଈ��d��:8jG�d��? << stream /Font << 12�12�1+�2� ��0��*�11U110 � �1U[0V1[U710�1U1[��b��\[[U[[V[U[\��ҫ��Ͷ��ӱӱ�ұ��\[[[��Ჱ��ᬱ�Წ��ᬱᬱ��ᬇ᱈�૱߫��ሬ��ለ��ሬ��]�]\]]�]]]��]]�c]]]?]? >> /ProcSet 2 0 R ��* 1T[U��^��d�]�^c�]�^c��d�^��d��d�^�^�^^�^^�^^�]]�]^]�^]]�d]�]�c�]��c��c��c��્��౱౫��]��]�]\]W]\]]�]�]�\]�\]�]]�]��^c��ᬉሎ��ራ��߇��b+��0 Therefore, th) Tj 7.0982 Tc 0 Tw (e) Tj 0 -13.08 TD -0.0184 Tc 2.7784 Tw (effect of potential predators on breeding roseate terns should be evaluated an) Tj 6.48 Tc 0 Tw (d) Tj 0 -12.96 TD -0.0221 Tc 0.3221 Tw (appropriate management techniques implemented to prevent or deter predators) Tj 9.24 Tc 0 Tw (.) *�� 0000254379 00000 n >> Tj 0 Tc 8.64 Tw ( ) Tj 290.76 0 TD /F0 11.04 Tf -0.0235 Tc 1.3435 Tw (Governments an) Tj 6.48 Tc 0 Tw (d) Tj -290.76 -12.96 TD -0.0133 Tc 0.3187 Tw (agencies with jurisdiction over roseate tern colonies should become involved in th) Tj 7.0982 Tc 0 Tw (e) Tj 0 -12.96 TD -0.0167 Tc 0.2383 Tw (education of the public on the importance of protecting this species and adhering t) Tj 6.48 Tc 0 Tw (o) Tj 0 -13.08 TD -0.0191 Tc 1.8845 Tw (Federal or local regulations. Kale, ed. The Roseate Tern is a bird of elegant proportions and dazzling white breeding plumage, accented with a black cap, dark bill, and pale rosy breast. /Type /Page 0000253821 00000 n ��11*��21+21+2�12a��b1�c�b,�౲��Ա��Ӳ��Ա��଱�ᱲӸ�Ӹ��Ӹ�ԸӸ�Բ��Ჲ��଎�ᱫ��Ӳ��W2]��ٲ��ٱ��\�[y�[VZVU7�U��ଇ��᳈��쳳��Ჭ��^��^��ር��d��c^�d]^�d]]]]W8W8V3�W822W222� 0000254799 00000 n Roseate tern. >> >> The Birds of Aruba, Curacao and Bonaire. ��* @@c@cdcdcdcdcdc^�d]c�]��߇]��߇��߇��81�� Tj 18 -12.96 TD -0.0141 Tc 0.4341 Tw (The FWS, DO) Tj -0.8654 Tc 0 Tw (T) Tj -0.018 Tc 0.474 Tw (, and DEP are developing plans to establish a roseate ter) Tj 6.48 Tc 0 Tw (n) Tj -18 -13.08 TD -0.0182 Tc 0.7936 Tw (nesting colony on a section of the abandoned U.S. 1 bridge near Pigeon Ke) Tj 6.48 Tc 0 Tw (y) Tj 0 -12.96 TD -0.0171 Tc 0.2871 Tw (just west of Marathon, Florida) Tj 9.24 Tc 0 Tw (.) 8058 �� +�+�+*� The history of the northeastern population has been summarized \(Nisbe) Tj 8.9309 Tc 0 Tw (t) Tj 0 -12.96 TD -0.0181 Tc 0.8447 Tw (1980; 1989a, Gochfeld 1983, Kirkham and Nettleship 1987\). On Culebra and the ) Tj -0.6509 Tc 0 Tw (V) Tj -0.0193 Tc 0.7393 Tw (irgin Islands, the birds constantly shift location) Tj 7.7054 Tc 0 Tw (s) Tj 0 -12.96 TD -0.0331 Tc 0.1381 Tw (from year to year, both within the U.S. ) Tj -0.6509 Tc 0 Tw (V) Tj -0.0212 Tc 0.1172 Tw (irgin Islands \(USVI\) and between th) Tj 7.0982 Tc 0 Tw (e) Tj T* -0.0257 Tc 1.2257 Tw (USVI and British ) Tj -0.0421 Tc 1.2121 Tw (Virgin Islands \(BVI\). /F2 10 0 R 0+01 1 �U[�U�0�0U[\�a��b[�[U[U[[��ҷ�ӱ�رӱұ�ұ��ӷ��[��౫��ᱱ��Წ�Წ��ᬲ��ᬱ�Წ��ሬ��્��ᬎ��ᬎ��ሬ��ሬ��ራ]�]�\W�]��]]��]c�]]c]?]? Although bot) Tj 6.48 Tc 0 Tw (h) Tj T* -0.0158 Tc 1.8558 Tw (populations experienced severe population declines, it i) Tj 7.7054 Tc 0 Tw (s) Tj 0 -13.08 TD -0.0178 Tc 0.1207 Tw (believed that the northeastern breeding population is unde) Tj 8.3237 Tc 0 Tw (r) Tj 0 -12.96 TD -0.0173 Tc 0.2573 Tw (greater threat) Tj 9.24 Tc 0 Tw (.) Rare an) Tj 5.82 Tc 0 Tw (d) Tj -223.2 -12.96 TD 0.0196 Tc 3.5504 Tw (Endangered Biota of Florida vol. Tj 0 -13.08 TD -0.0183 Tc 0.4623 Tw (Among the direct impacts are predation, storms, tidal inundation, flooding, o) Tj 8.3237 Tc 0 Tw (r) Tj 0 -12.96 TD -0.0155 Tc -0.2245 Tw (prolonged periods of cold wet weather which destroy the nests, eggs, or young) Tj 9.24 Tc 0 Tw (.) /Contents 44 0 R Tj 18 -12.96 TD -0.0192 Tc 0.7392 Tw (They have been identified during migration in several coastal counties i) Tj 6.48 Tc 0 Tw (n) Tj -18 -12.96 TD -0.0169 Tc 1.8769 Tw (Florida. 1,�+ 34 0 obj endobj BT 198.12 685.92 TD 0 0 0 rg /F0 9.96 Tf 0.0115 Tc 1.6985 Tw (U.S. stream �� /Type /Page If the MDIFW evaluation determines that significant alteration of the habitat would occur, a state agency or municipal government shall not issue a permit or license for the project. *��+W�ᎍb7�� /ColorSpace [ /Indexed /DeviceRGB 255 11 0 R ] /Parent 5 0 R Roseate Tern Nesting Sites Background. *+228V21��+ �1�V��ᱲ��Ա�Ჱⲱ��౲��᫱�ӷӱ��Ա�ӱӸӱ��ӱᱱ��᫇��10��1 1[��ٱ�� 㸲Բ��]��ሬ��߇��\[V[��U7U�U11 2U�[V�b��ሲሬ��⬳��ᳲ��ⲳ��⬏��^�^��ር��ᬈ��ሉ��d��ሏ��]�W72 ��2�V\[2��ԸԎ��૱��߇��౱��Ӱ��આ��\\V1210�01 1[ޅ��ӱ�Ը�ٸ��Ӹ��᱇��߀��\[V�U7U�1U11U1U�[V\[�\��߈��ᲈ��ᳲ��⳸��ለ��d��]�3\2,�� /Count 16 /Type /Font 6725 17 0 obj � Itâs with the help of tremendous humans, that the roseate tern is making a â¦ Tj ET 96.12 46.68 75.96 0.48 re f BT 0.9955 0 0 0.9955 96.12 32.64 Tm /F1 10 Tf -0.0887 Tc (Pag) Tj 4.4429 Tc (e) Tj 47.1341 0 TD 0.0281 Tc (4-44) Tj 4.4429 Tc (4) Tj ET BT 1 0 0 1 60.12 728.64 Tm /F1 9 Tf 0.4037 Tc (ROSE) Tj 0.3202 Tc -0.542 Tw (ATE TER) Tj 2.5017 Tc 0 Tw (N) Tj 268.1427 0 TD 0.4422 Tc 0.2478 Tw (Multi-Species Recovery Plan for South Florid) Tj 3.9954 Tc 0 Tw (a) Tj ET 59.16 745.68 486 0.48 re f 59.16 717.6 486 0.48 re f endstream >> Please contact a Regional Wildlife Biologist at the nearest regional headquarters. 0�� 60 0 obj Tj -18 -15 TD -0.035 Tc 0.065 Tw (Trull, ) Tj -1.0978 Tc 0 Tw (P) Tj 0.0139 Tc 0.0694 Tw (. ��*0*[U��V�\�\�ހ]��ށ]߁c�]�߁]�]^�^�]�]�]�]��]��c��c��c��߇��્��᪍��ఫ��ށ�]�]߁�߁c��ሲ��ሲ��ለ��ଇ��߇��c��b��߇�߇��߇�� No. Tj -18 -15 TD 0.0215 Tc 0.4085 Tw (Kirkham, I.R., and I.C.) Roseate terns may use artificia) Tj 8.3309 Tc 0 Tw (l) Tj 0 -12.96 TD -0.0132 Tc 0.9732 Tw (colony sites) Tj 8.64 Tc 0 Tw (.) /Resources << << Tj T* -0.1287 Tc 3.5847 Tw (Nesting sites may be densely vegetated or bare \(J.Saliva, FWS, persona) Tj 8.9309 Tc 0 Tw (l) Tj 0 -13.08 TD -0.1267 Tc -0.1133 Tw (communication 1997\). ) These structures would also provid) Tj 7.0982 Tc 0 Tw (e) Tj 0 -13.08 TD -0.0169 Tc 0.2809 Tw (nesting opportunities to least terns, a state-listed threatened species in Florida) Tj 9.24 Tc 0 Tw (.) BT 198.12 685.2 TD 0 0 0 rg /F0 11.04 Tf -0.0203 Tc 1.1903 Tw (and most first year birds generally do not migrate northward, but remain o) Tj 6.48 Tc 0 Tw (n) Tj 0 -12.96 TD -0.0189 Tc 0.2989 Tw (wintering areas \(Nisbet 1984\)) Tj 9.24 Tc 0 Tw (.) *+��0��0+*��0*��U2��dji@j�dꎲ��jjdjFkjc8*�� /Font << << /F1 9 0 R 19 0 obj The wing chor) Tj 6.48 Tc 0 Tw (d) Tj 0 -12.96 TD -0.1262 Tc 0.4426 Tw (averages 23 cm in length; its wingspan is about 60 cm. ��++*�+0+�1+101 1UU�U[U�U[U2[U � �U[U�U[[y�7*��*0� [ya[[�Z[��]��]��]�]�]�]�]�]�c�]�]��]��c��߇�c��އ]��߁c��߇��઱��ߪ��߆��ሎ��ሲ�ሲ��ሳ�ሬ��ለ��ራ��߇��߇߇߇��߆�]��]��2�2�++��+*� /Contents 70 0 R �� Tj 88.68 0 TD /F0 11.04 Tf -0.0198 Tc 3.3078 Tw (More intensive studies including food availabilit) Tj -0.72 Tc 0 Tw (y) Tj -0.0427 Tc 3.4027 Tw (, hatchin) Tj 6.48 Tc 0 Tw (g) Tj -88.68 -12.96 TD -0.0137 Tc -0.2023 Tw (success, fledging success, causes of mortalit) Tj -0.72 Tc 0 Tw (y) Tj -0.0143 Tc -0.1957 Tw (, interspecific interactions, and impact) Tj 7.7054 Tc 0 Tw (s) Tj 0 -12.96 TD -0.0169 Tc 0.2809 Tw (of contaminants on breeding terns should be included in these studies) Tj 9.24 Tc 0 Tw (.)