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. " . ",
MOTE MARINE LABORATORY
pri118.2006
1r. 1ichael G. Heyl
(.hoND'" fhrbor •
Kry w." Co .... h &/ry fa"" • 'WOk I't'lWlC"IIJru" plJr/t · lropi~al RC-UAr~b l41bcr.,ory-
c r:: yP 1r < f 1 ~v"m /1'., til-
outlw.est Florida Water Managern niDi Iriet 760 1 U .. . I ligln ay 01
ampa, FI. 3363 7-67 9
Re: Distric t Purchase egetaLion ur e\
Dear r. li e I:
'1 hi two-part r port descri be _tudies conducted b) r . orne t E °le\ z and Brad Ro hbins on mo llusk and horeline lype \\.ithin the nc lo te River. "I his tud. is part of lh\! , outhwesl Florida Water Management Di tri t" . program to de ~ribe west-central f lorida tidal river t'or the purr se o f e tab li hing regulator) minimum fl o\.\. . in each.
I he project call d ~ r li v~ and dead mollu~ks to be a ss >d using rapid urvey technique mparabl to tho ~ pr .. iou. l. u ed bj otearine I aboratory in tudi s of the Peace . . 1\) akka. ek i Wa -he and lafi.a Ri\ ers, h II reck, and cKay, Dona. nd Rot ert Bays. . "wi nd hieId" . une)' oC the nclote Ri ver' hore line coupled \-vith
an as es ment or aerial photograph. and lancluse map wa u ed to delineat the Ri 'er ' horeline b) I)pe.
Pl ease ac epl the enclosed material s a a final letter report of fi nding for the it cI ffo rt.
c appre iate the oppol1unilY to haw conducted lhi inlere ling. tud). and hop rh Oi (ricl rind il useful in lIs work .
Llnest D. I: tev Di rector
ente r for (oastal hology
~~)~" :> Brad le) D Robbin: ivlanager I and cape Eco log) Program
• f
Robbin horeline Mapping
Part One: Mollusk Surve '
Rapid- urvey meth d were employed fr m De ember 12, 2005 to February 10, 2006, to cen us the macro-mollusk communi tie of th An I t Ri ver, lorida. The Anclot Ri er wa ampled from it mouth to ri er ki lomet r (RK) .0 on on ki lometer interval · then on half ki lometer intervals t RK 12.0, and th n at RK 13, 14, and 15. A Distri ct RK map a u ed to 10 ate tat ion and al l ampled ite orre ponded to it defined by the
cope of Work, e cept that RK 11. was rno ed to RK 11.3 to avoid local human di turbance . Be au e RK 16 was not ampJed a per the Pur hase Order, a replacem nt effo rt was made at RK - 1.0.
Becau e the primary objecti e of the rudy was to identi fy down- tream pattern in p cie di per ion, amples were collected aero each tran ecl at representative sites,
and data were poo led for the en tire tran ecL In ingle-channel reache , ubtidal am ples wer collected clo e by opposite bank and at e enly paced intervals acros the channel. In reach s wi th mar hiland and mUltipl e channels, ubtidal effort was distributed 0 as to ample in each channel or bas in.
ollection of intertidal ample was biased by two criteria. Fir. t, accreting banks were preferred over eroding o ne , meani ng in practice that the in ide of bend were pr ferred o er out ide , and that ample were lIecled more from poi nt-bar mar h i land and hoals than from teepl incl ined banks. Second, a preference wa mad for the bank
j udged to be lea t altered b human activity. ea wall and fill ed area were avoided where po ible.
ubtidal ample MLW) were ollected by a petite ponar grab rather than pipe cor becau e larger mollu ks are often mi ed or I t by the core . Ponar grab offer a larg r ampling urface area (0.02 2 quare meter ) than pipe cores (0.00456 quare meter ). A ample was comprised of one ponar grab at a given location . Five su h ubtidal ample
were taken in di fferent en vironment along each hal f-kilometer tran ecl givi ng a pertran e t ampl ing urface area of 0. 11 6 quare meters. ontent of each ample were concentrated 0 er a 3.0 millimeter sie e and proce ed in the fie ld. n\mown were bagged and r turned t the Lab ratOl for identi fi cation.
Intertidal ample (> MLW u ually wer colle ted by pade although p nar grab were u ed in areas wh re the ub tratum a unfi t for wading. Intertidal effort as th am a ubtidal effort e cept that hand co ll ection f parti cular peci w r added to intertidal ample 0 a to record th pre en e of rare or cryptic specie . The ga tr pod 'i'.
eritina and Littoraria for example, are often found in low number , near the top of black n edlerush hoot . Oy ters and mu el likewi grow cryptically b hind mangr e root or within cre ·ce offa llen wood.
Where a fe t do 0 , ubtidal area wer al 0 vi ually rec nnoitered b ad ing or n rkel ing and intertidal area were walked in earch of rare occurrence .
p cimen were orted a Ii e r dead and identi fied in the fi eld r Laboratory. rea h
2
Robbins - horeline 1apping
pecie in each ample b th Ii e and dead median ize wa d termined by arranging specimen from malte t to large t and measuring th median p cim n to the near t millimeter. a tropod w re measured fr m the ape to oppo it end' bi al e were measured from front end t hind end . For data ana l i , a mean value of median ize was computed for each p eie. Thep rcentageofju nil «IOmm)ifanywa recorded by peele where identification was po ibl , ~ r live and dead lot at each tran eel. ondition wa cored for each whole Ii e animal or ingle dead alve a percent co ered by mechanical ro ion, sh n di olution, or oth rIo s or damage.
Findin
An cel spread heet of all pecie at all tation i pr vided in Attachment I . Thi Report contains graph depicting data for indi idual peeie that were numerous enough t warrant d cripti n, an xhibit e tion for other p cies, and graphs depi ting ummary community data and the palial arrang ment of pe ie a a fun lion of river
kilomet r fI r both ri ers.
A total of taxa were colle ted. Sp ie ri hoes wa high, e en in compari on to oth r tidal tream in outhwe t Florida that ha e been tudied by the arne m thod. pe ie richne value for oth r tern are II in hell reek, 15 in the Weeki \ achee River, 20 in th Alafia River 24 in the M akka, and 4 in both th Pea e and DonaIRobert Sa y tern .
The moll u k fauna of th nclote Ri er i simi lar t that of oth r tudied tream , in tenn of their pe i mpo ition in 10 - alinit r a he . h lower n lote, on the
ther hand, upport a number of sp ci n t found in other r ently- tudied ri er . Th additional pecies reflect the proximit of the river to Andote An horage, wh re condition ar favorable Ii r a producti e and di er e mol lu can fauna. The lower Andote Ri er i m t imilar t the DonaIRobert Sa s area in thi regard wh r the Gulf of M xico i al immediately adjacent.
[n tenn 0 peele abundan e th ja kknife clam Tage/us p/ebeiu , was mo t common . Tage/lis i an exc Hent indi ator ofth tidal ri er community. nly n mu el pecie , Geuken ia demis a , wa common but tw other intertidal peci Pof mesoda caroliniana and Liltoraria irrorala , al 0 were abundant. , ho n in the foil " ing Ii t, oyster wer ommon in c mpari n to other spe ies but thi rank i an artifact of th ir <?
high number in reef: .
Rank Order bundance of Mollu k pecies in the Anclote Riv r.
pecle
ra 0 trea IrglTlIca Molgulida Tag lu plebeiu Geukensia demi a Polym oda caroliniana Mulinia lateral i
luone can ellata Littoraria irrorata Laevi ardium mortoni Tellina tampaen i I chadium recurvum Carditamera floridana Na anu ihe Anomalo ardia auberiana Anomia implex
repidula plana Anodontia alba Argopecten gibbu Bull a triata Luci nj ca na ula Mel ogena or na Prunum api inurn
erithium mu carum onu ja pidus team i
Polinice duplicatu Brach iodonte e u tu
nsi mmor Rangi a cun ata Amygdalum pap flum Arene tricarinata Atrina rigida
orbi cula manilien i Laevicardium lae igatum Lima p Ilucida Mactra fragil i Melampu ffeu Mytilop i leucophaea ta Trach cardium gmontianum
urbo ca tanea
4
otal
276 142 11 2
71 62
6 3 1 3 1 2 2 27 19 15 10
8 7 5
4 4 4 3 3
2 2 2
Percent
2 .78 14.81 11.6 7.40 6.47
.75 3.23 3 .2 2.92 2.92 2.82 1.9 1.56 1.04 O. O. 3 0.73 0 .52 0.52 0.42 0.42 0.42 0: ' 1 0.3 1 0.3 1 0.2 1 0.2 1 0.2 1 0. 10 0.10 0.10 0.10 0.10 0. 10 0.10
.10 0.10 0.10 0.10
Robbins h r line Mapping
Cumulati ve Perc nt
28.7 43. 9 55.27 62.67 69.13 72. 9 76.12 79.35 82.27 85.19 8 .0 1
9.99 9 1.55 92.60 9 .43
4 .26 94.99 95 .52 96.04 96.45 96.87 97.29 97.60 97.9 1 98.2" 9 .44 9 .64 98 . 5 98.96 99.06 99.17 99.27 99.37 99.48 99.5 99.69 99.79 99.90
100.00
Robbins horeline Mapping
The Anclote River fauna is comprised of many pecie that were represented by deadonly material, e en when An lote nchorage Fauna are di counted. De pite e tra effort to identify and cen or relict or fo il material, a few of the dead-only reports may repre ent ntamination of th modem fauna. The Andote Ri er we t of . . Highwa Alternate 19 has be n dredged extensivel , ex.po 'ing and spoiling much old material a ubtidal and intertidal fill , and a eroding poil island .
Compared to other outhwe t Florida rivers studied b similar method , An lot Ri er mollu k collection t nded to produce ma LI pecimen that occurred in low densitie and over horter reach of the river. Con idering these tendencies along with high pecie ri hne. , Anclote Ri er fauna may b shaped by constant but low levels of succe sful recruitment, Follo ed by 10\ growth or high mortality prior maturation. Rea on for mall molluk size densitie , and ranges are not e ident from the collected data.
Low den itie rnak interpretation of indi idual species data di fficult when 0 tI \ station were occupied. The introduced, naturalized and inva i e species orbiettla manili nsis was found as dead material at RK I 1.3, but may not occur in the ri er's up tream reach 0\ . ing to teep channel banks and unsuitable ediment c ndition at depth .
The subtidal clam Rallgia cuneata wa al 0 found at only one tation (RK 15.0) but i probably a table element of the fauna because it \ a collected as both Ii e and dead material and a very large pecimen . One live Rangia mea ured 76 mm and i the large t li ve Rangia pecimen collected to date in mollu k survey in outhwe t Florida. Mu el pecie that tend to occupy broad river reache el ewhere occur at one or twu tation in the Anclote River, and except for one pecie di cu sed below mu el are not
ad minant element of the An lote' s mollu can fauna.
Tage/u was pre ent a Ii e and dead material. Their hells are fragi le 0 it i reasonable to a ume that the material wa recent. Highe t densities were from RK 4.0-6.5 and large t Ii e and d ad hell were upstream fRK 5.0 (Figure I). Geukensia demi sa wa the on l mu eJ to occur in high den ity or occupy a sub tantiaJ reach of the ri er. Thi mostly intertidal pecies wa most abundant down tream but large t, upstream within it II kilometer reach igure 2 . Another intertidal pecie , Polymesoda caroliniana, wa ommon in the upper half of the tidal river and, like Tagelus, was mo t abundant
down tream but large t, up tream within its reach (Figur 3) .
y ter \ as encountered at I tation between the ri er mouth and RK 9.0, but their range and abundance i imperfectly de cribed b ampling on half or whole kilometer intervals. In general , mall and mostly dead oy ter reef: 0 ur at and near the ri er mouth and lower fev kilometer , but large li ve reef: are mo t conspicuou from RK 4.0 to RK 7.0. Reef: then become mailer and more wid \y spaced up tream t near RK 9.0. Intertidal oy ter were more common than ubtidal one and like the other intertidal pe ies, were mo t abundant down tream but large t. up tream wi thin its reach (Figure
4).
Robbin horeline Mapping
One p ie colle ted in ery high number wa not a mollu k but i rep rted her becau e it pre en orre ponded with a paucity 0 mollu k , and lik many clam , it is al 0 a filter-feed r. A oft tuni at in th Famil Molgulidae repre ent d about I percent of th t tal pecim n count. It w primaril ubtidal, only fi und aJi e, and ery abundant in off- hannel areas betw en RK 3.0 and .0 (Figure ).
Di tributi n patt rn for the combined fauna ar intere ting. Attached graph d pi t th dispersion of sp ci in relation to ri er p ition, u ing variou attribut . ort of pecie occurren e b up tream r d " n tream appearance (Figures 6. 7) show trong
changes characteri tic of rapid rate of communit tructure evolution. Th marine mmunity of Anclote Anchorage i di tin tive. Once within th ri er th lower river
fauna shift near RK 4.0 and then diminish with up tream di tan . Abo e RK .0 a ri erine low alinit community pre ail .
down tream " ag" appear in p cie ri lme near RK 2.0 (Figur 8,9), and i evident in faunal den itie io the RK 1.0-3 .0 reach (Figures 10, II). Thi depre ion in di ver ity and den it i not regarded to be a property of th natural moHu k mmuni ty but rath r the effect of ever habitat limitation impo d by exten ive dredging and spoiling, and the effect of a high energy en ironment creat d by boat wake . On balan e, harp d lines in abundance from RK 4.0 t 5.0, and harp decline in di er ity from RK 5.0 to 6.0 are con id red to be the re ult of naturall occurring changes in communi ty tructure.
Remark
The Anclole Ri er pre en a di ver e fauna r lati ve to other tidal tern tudied by imilar method . The pre ent urve depict a fauna compri ed of many mall and often
dead p cim ns of many pecie , most of" hich occur in relati el short ri er rea he . pecie replacement rate are high a a fun ti n of ri er location (Figure 12 . An
authentk tidaJ river fauna occur in the An lote Ri er, primarily from RK 7. to RK 11 .. It is bracketed by a down tream estuarin and an up tream oligohaline fauna. An apparent ' sag" in down tream richen s and den ity i on idered to be th on equence of habitat con traint . The con traiojng effect f tuni ate comp tition, heavy algal a umuJati n at orne tati on , and poor edi ment probably a count for orne f the pattern ob erv d in Anclol mo llu k fauna, pecially in off-channel and back-ba area . Dynami mean , ranges, and extreme of alini ty along the tidal river may also contribut to the ob rved re ult though no alinity data were collect d in th pres nt effi rt . fi'.
6
Robbin ' horeline Mapping
\ 0 station with po ition not spe ifi d by the Anclote Ri er lcilometer map are:
RK Location -1.0 Anclote An horage 1 I . Anc10te Ri er
Exhibit
Latitude 2 .17786 28.172 16
Graphs of mollu k pecie data for pecie with low occurr nc s.
Attachment
Longitude 82. 1018 82.72421
I. cel file, " Ancloteclamdala"- pecie occurrence , den ity, ize, ju eni les, and ndi tion.
7
Robbin horeJine Mapping
Tagelus plebeiu • Live 0 Dead
Intertidal ubt idal 100 r--
('l 80 0
E 0 ... 0 c..> 60 0 ce 0-...
~ d)
40 ..0 0 0 0 E
::I 20 • 0 • Z .ce . • 0 «:> • o:xo 0 0 0 0 T r ,- T ,--
50
1 40 0 --- e e j s 30 • Qt E 0 '-'" o (j) . ,p Q) 20 0 o cP cR o o • CI'l .. 0 0 10 0 0
1 0 1 T rJ
100 0 0 VJ Q)
s:: 80 Q)
> 60 ::I ~
t:: 40 I Q)
~ 20 0 j Q)
0... 0 0 0 ... ~ T • €9 ~ ..
10
J x: 8 o 0 000 0 Q) o 0 "0 o 0 0 0 6 00 00 0 -...
0 0 00 Q)
.s 4 • I • 0 ctl Q)
•• ~ IF.
~ 2 • •• 1 • • 0 L 1 T
0 5 10 15 0 5 10 15
River Kil ometer igure I: Habitat, den it and condition data for rage/us plebius .
Robbin hordin Mapping
Geukensia demissa • e 0 Dead
Intertidal ubtidal 120
J f N 100 E ~ 80 • C1) • c. ~ 60
1 ~
C1) 0 .J:J
E 40 0 • 0 ~
z 20 «:> 0
T J 1 -1 . 0 • 0
0 • <» ,. T'
80
1 j 60 0 ~ -<
'? • • E 0 o ~ '-' 40 • • • C1)
0 ~o o (/) 20 •
0 -,- -r T
100 r 1 I en v '5 80 v > 60 ::l -. ....
40 c:
j C1)
• 0 u ~ 20 j C1)
p.,
0 T -,-e-~re • <:.
10 ~ 0
>< 8 0 v v 000 0 ..s 6 -<
1-0 0 0 0 v ...c: 4 • • ...-<a C1) • Y: ~ 2 • c.. • • 0 1 r
0 5 10 15 0 5 10 15
River Kilom ter Figure 2: Habi tat, d n ity and condi tion data for Geuken ia demi a.
9
Robbins - Shoreline Mapping
Polymesoda caroliniana • Live 0 Dead
100 lnt rtidaJ ubtidal
N 80 0 E 0 '-~ 60 0-'- J
0
. ~ o~ ~ 40 .D
E CO 0 ::l 20 ~ Z 0
•• • 0 T -, -,
60
r 50 • -i
---- 40 • § .O~ 00 • '-' 30 0 ~ 0 0
, 20 (I)
j 10 0 T T T
100 r VJ ~ ...... 80 ::: v > 60
1
::l --, ......
40 ::: ~ u ~ 20
0.-
0 r .- ~.ee • T - T
10
~ 0
1 x 8 o 0 -l Q)
0 000
0 -0 J s:: 6 o • ! 0 '-
I ~ • 1 -5 4 • • 0 I ro Q) •
I ~ ~ 2 • 0 1 1 r T
0 5 10 15 0 5 10 15
Ri v r Kilometer Figure 3: Habitat, den i and onditi n data for Pol mesoda caroLiniana .
10
Robbin horelin Mapping
Crassostrea virgillica • Li e 0 Dead
Jnt rtidal ubtida l 500
l N 400 • E
-<
l-(\) 300 Cl. ....
0 I (\)
200 .D 1
E • 0
j • ;::; 100 o ~ o . ~ 0 Z
0 L dt · e«) 0 1" Q ·fiiI T ----0 0 .,. 1"
80 r j •
60 1
• ..-- • 0 != 00 E
I • • 40
o . o o. ~ 0 I 0
(\) 0 .!:::l 0
CIJ 20 00 . ~ 0
0
0 T T T T
100 V) (\)
~ 80 (\)
> 60 ::l ......, ....
40 c: (\) c..l
0 I- 20 (\) • 1 ~ • • 0
0 Epoe . ~". ea3 1" e ~ • 10 r
>< 8 0 0 0 00 • (\)
'"0 0 .5 6 o 0 0 ...
0 0 0 0 (\)
..c: 4 •• 0 0 CQ (\) • •• • (f.
~ 2 1 • •
0 0 5 10 15 0 10 15
Ri r Kilometer Figur 4 : Habitat, den i ty and conditi n da ta for ras ostrea virgini a .
11
Robbin horeline Mapping
Molgulidae • Li e pp.
0 Dead
InteJ1idal ubtidal 500
N 400 • E .... ~ 300 • 0.. .... • (:)
200 ..0 •
J E
I ;:s 100
]1
;z: • 0 L • - , T 1 T
30 • ..-. • E
20 • • E • '-' • I!) , (/) 10 -j •
0 T
100 - • CI) I!)
c: 80 I!)
> 60 ~ ::::I ...... ..... 40 c:
I!) <.) ....
20 I!) • 0..
0 . ] ~-- I
10 T
><: 8 I!)
"'0 c: 6 .... I!)
.s 4 <'l I!)
<f. ~ 2
• _. 0 !
]
0 5 10 15 0 5 10 15
Ri er Kilometer Figure - : Habitat den ity and condition data for Molgul ida p.
12
Robbins horehne Mapping
Rangia cuneala orbicula mani li n is
Myti lop is leucophaeata Lima pellu ida
Polyme oda caroliniana Tra h cardium egmonlian um
Bra hiodonte ex ustu Melampu orreu
Am gdalum pap rium Lae icardium mortoni
Geuken ia demi a repidula plana ' as ari us vibex
Molgulidae Li ttoraria irrorala hadi um recur urn
n is minor nomalocard ia auberiana
Lucinisca na ula T lI ina lampaen is
Mulinia lateral is agelu plebeius
Prunum apicinum Polini duplicatu
Melongena corona rassostrea virginica
Atnna rigida Anodontia a lba Turbo castanea
1a tra fragi li Laevicardium lae igatum
nu jaspidu teamsi hione cancellala
eri thium mu carum arditamera fl oridana
Bu llatriata rgopeclen gibbus Arene tricarinata
nomia simplex
Anc10te River r r
.... ...... ..... .... .. ...... .... .... .... ........ ..... .. ···· ··· ·0 ······ ··· ····· ····
................ .... ..... .. ..... ..... ... ....... ...... .. .• .... .. .. .. .. .... .........
.. ...... ... ....... ..... ............ ..• ... ....... .. ... .. ... ......... .. ... .. .......
........ .... ...... ... ..... .... ..• .. ....... ·0·0 ······· ·· · .. ········ ········· ·0 ······· ·· ·········· ··· ·· ..... .. .. .... . ... . .. ....... .. .. ..... .. ..... ·· ···m ···· ··· ······ ······ ·· · .. ··· ·· ·· ·· ·· ············· ··· ·· ·· ···· ······· ··· ·······0· ·· .. ·· ··· ···· ··········· · ... .. .......... ........... . .. ... ..... .... .. .... ... .. ·0 .. .. · .. · .. .. · ........ ·· .... .. ·· ...... .. · .. .. ...... .. ..... ..... ........ ... ..... ~ ........ ..... ..... ....... .. .. .... ... ..... ... . .. ............ .. .. .. .. .... .... .. .. @ .. .. . ... -w .. .... .... .. ...... .. .. .. .... .. .......... · .... ·0 · ..... ....... .. .... .. .. .......... ...... .. ... ..... .. ...... ... .. .... .... ..... .. . .. ..... ..... ....... .. ............ ........... ... .. . ..... ... .... .. ....... ....... .... .......... ........ .... ... ....... .... . ..... .. . .. ....... .. ........ ... ..... . .. . ...... . ... .. .. .. .............. .. ...... .... ..... .. .... ...... .. .. ........ .... ...... .. ... .... .. ........ ... .................. ····· ·· .. · .. ·· ··· .... ·• .. 0 ··· .. ·· ·· · .. ··· .. ··· ····· ··· .. ·· .. .. ··· .... ......... . .. · .... .... .... .. .... 0 · .. . ... ..... ...... .................. .. ... ..... ...... .. . .. ·· ··· ········· ·· 0 .... ·· .... ···· .. · .. ···· .. .. ·· .. ·· ·· .. ··· .. ··· .. ........... ... .. . ···· ···· ··· o .. · ...... · ·~· ·· .. ···• ·· ·· · .. ···· .. · .... · .... .. · ...... ·· .... . . .... ..... ·@ ·o· · . .... .... ............ ......... .. .... ............. .. ..... .. ..... @ .. .. .. .......... .. . ......... .. .... . . .... .. ........ .......... .. ... .. ...... .............. .. ........ .............. .. ........ .. .. . .. ·· .... · .. .... .. ·0 .. · .. · .. ·0 .. · .... .. .. · ...... · ............. . .. .. .. .. ·0 .. ...... .. .. .. .. .. ·0 .. .. .. 0 ...... · ....................... .. . .... · @ o· @ .~. . .. .. .. ...... .. .. ............... . .... · 0 .... .. .. .. .. ...... ..... .. .. .. .. .. .. ...... .......... .... .............. .. ...... 0 · . ........... · . .. 0 · .... ·0 ........ .. .................. .. . ·0 · ........ .. .. .. ....... . ............ .... .. .... ... ........................ .. ·0 .. ........ .. .. .. .... ... .... .. .. .. ........ ..... .... ......... .. .. ............ .. ·0 ......... ... ... ....... ........ ......... ... ... .. ... .. ... .... ............... .. . ·0 ·0 · .. .. · ...... .. ...... · .. · · .... .. ............... .. .... .. ...... ........... . ·o ·@ 0 .. .... .. ·· .. · .. · ........ ...... ....... .. .. ... ... .... .. ......... . ·0 ·0 .. ............... ... .. .... .. .... ...... .. .......... .. ... .. .............. .. ·o ·@· .. .. ·o · .. ·· .. · .... ······ ·· .. ·· · .... ···· ·· · .. · .. · .......... ····· ...... .. .@ .. . .. .. .. .......... ........ .. .. ...... ....... .. .. .. ... ............ .. ..... .. .@ 0 .... .. .. .... ............. .. ........ . .. .... .. .................... .. ·0 ·· .. .. .... .... .. .... ............. .. .. ... ..... ... .. .... .... .. ................ . ·0 · ........ .. ...... 0 .. .. · 0 .... .... .. .. .... .. · ·0 .. .. .. .... · ..... .. IlL I 1. 1
o 2 4 6 8 10 12 14
Ri er Ki lom ter
e • Dead 0 Both
19ur 6: p tream sort of speci soc urrence for Ii e and dead materi al b n er jlometer.
'i.
Turbo ca tanea Ma tra fragilis
Laevicardium laevigatum Arene tricarinata
Prunllm apicinum onu jaspidu steam i Cerilhium mll carum
Atrina rigida Argopeclen gibbu
Bulla triat a Lucini ca oassula
arditamera f1 0ridana I chadium recurvum
Mulinia laterali nSI mInor
Melampu coffeu hione cancellata
Anomalocardia auberiana Amygdalum papyri um
Trachycardium egmontianllm as ariu vibex
Lae icardillm mortoni Brachiodonte exu tus
Molgulidae Lima pellucida repidula plana
Tellina lampaensi Melongena corona
Polinices duplicalu, Anodontia alba
Littoraria irrorala ras ostTea irginica
Mytilop is leucophaeata Tagelu plebeius
Geuken ia demi a Anomia imp lex
orbicu la mani l iensis Rangia uneala
Polymesoda caroliniana
Robbins horeline Mapping
Anclote Ri ver T ----,- ---r- T r
·0 ················ ···· ·· ····· ·· ···· .. ···· .. ···· .. .. ····· ·· .. ......... ........... . ·0·· ·· .. ············ ·· ··· .... ·· .. ····· ······ ·· .... ····· ...... ·· ................. . ·0 ·· .. · .... ········ .. ···· ······ · .. · .. ·· · .. ·· .. ··· .. ·· .... · .. ·· .. ··· .............. . ·0····· .. ············ .... ······ ··· .. ·· ··· ···· .. ·· .. ···· .. ··· ..................... . ..... .. .... .... ...... ..... ... ..... ... .... ... ......... ............................. ·0 ·0 ······ .... ···· ···· ···· .. ······ ··· ········ .. ·· .. · .. ··· .... · .......... ...... . ·0·0 ·· .......... ............. .. ....... ........ ............................... . ···· ··0 .. · .. · .. ·· ·· ······ .. ····· .. ··· ·· .. .. ·· · .. ········ .. ·· .. ·· ......... ....... . ·@ ·o · .. ···· ······ ·· ·· .. ······ ·· ·· ·· ······ .. ··· ···· ·· ...... ·· ....... .. ..... .. . .. .@ ... .... .. ... .. ..... ..... ... ... .... ......... .... .................... .......... . ·· .. ··· .... ····· 0 ···· ······ .. ··· .. · .. · .. ··· · .. · .... ·· .. ·· ...... ··· ·· ............ .. ·O· @·· .... O· .. · ...... · .... ...... .... · .... · .. · .. · .. · .......... · ...... · .... .. .. ... .. ......... .. ..... .. .. .... ............. .... ... .................... ... ......... . ···· .. · .... @·O·(l)· ...... ·· .. · .. · .. ··· ··· .. · .. ·· .. ·· ··· .. · .......... · .... ··· ... .... ... ...... ......• .. 0 ... .... .... ..... .................................... . .. ........ ... .. .. .. .... ..... -0 .... ... .... ........ .. ......... ...... ................ . ·O· @·O ·· .. ···· {XD···· · .. · .. ······ .. ·· .. · .... ··········· .... ··· ··· .... . ·· .. ··· .... ···· .. ···· 0 ·00 .... ··· ·· .. ·· .. ···· · .. · .. ··········· .. ··· ........... . .. ··· ...... ·· .. ······ ····· ···0·· .. ··· · .. · .. · .. · .. ·· ··· .. ··· .. ····· ............... . ··· ·· .... · .. ···· .... · .. ·· .. ····0 .. ······· ...... ······ .. ···· · .. ·· .. ·· ............. . .... .. ........... ..... ~ ... .. ...... .. ... ................................... .. ..... ......... ... ...... ... ~ .. ..... ... .. ..... ............ .................. . ...................... ..... ... . C() .... .......................................... . .................. ............. ......... ................................... .. .. .................. ......... .. .... ... .. ........................................ ........ · .............. · .. 0· · . .. ...... ... ...... .. .......... ................ . ........ · .. 0 · .. ..... .. ~ ... ...... ..... .............................. .. ······ ·· ··0· ···· ····· .... ·· .. -0 .. ····-0 .. ··· .. ·· .. ·········· ··· ............. . .. .. .... ...... · .... · .. · .. · .. .. ·-0 .. .... · .. 0 ............................. .. · .. ···0 ··· ··· ····· .. ···• .. 0 ·· .. · .. · .. ·0 ·· .. · .. ·· .... ·· .. · .... ······ ..... . .................. ..... ... .. . .. . .... .... . . ......................... ...... .. .. .. @ ·O ·@ ·@ ·~·@ · ... ............................. . ....................... .. ... .. .. .... .... .. ...... ... .. . ... ......................... ..... . @ .... ..... .... . .. ~ ................... . .... .. · .. · .... .. · ...... .. ·• .. .. ·~ .. · ·~·W .......... · ...... ·· ·0 · .. · .. · .. ····· ··· .... 0 ·· .. ··0·· .. .. .. .... ··· .. ·· .. 0 · .... ··· ········ .. .. ................................... ....................... ·· 0 .. · ...... · .. ...... .... ....... ..... ......................... .. ................. .............. @ ···· .... ·· .... · .... ·· .. ··· ·· .. ···· • · .. · .... ·~@·@·O ·o
1 L 1 1 J I .L
o 2 4 6 8 10 12 14
Ri er K ilorneter
Li e . Dead 0 Both @
Figure 7: Downstream ort of peCle ccurren e for Ii e and dead material b n ver kilometer.
14
Robbins - horeline MappiJlg
umber of peCle - i e and Dead 14 ,- ,-
12 Subtidal and lntertidal 1 C/j
v
j '0 10 v 0..
{/) 8 j 4-. I 0 .... 6 v .I:i E 4 ;:J
Z 2
0 1 -----.J __ .L ---L-
0 2 4 6 8 10 12 14 14 T T "I T
12 lutertidalOnly en v
'0 10 v 0..
{/) 8 4-; 0
~ 6 .I:i E 4 ;:J
Z 2
0 1
0 2 4 6 8 10 12 14
12 - -r- -,-- -,
10 Subtidal 001 en v 'u v 8 0.. {/)
4-6 0
.... v
.I:i 4 -" E ::l Z 2 -
fi'.
0 0 2 4 6 8 10 12 14
Anclote Ri ver Ki lometer
Figure 8: pecie richne by river kilom tef for Ii e and dead material combined.
15
R bbins horeline 1appmg
umber of Spe ie - ubt idal and Intertidal 14 T T T ~
12 Live and Dead VJ d)
'0 10 d)
0... f/) 8 ...... 0 .... 6 d)
.D 8 4 ;:l
Z 2
0 --L ~ 1 -L
0 2 4 6 8 10 12 14 14 T I ----r T- -r- -, 12 Live Only
VJ d)
u 10 d)
0... f/) 8 ...... 0 .... 6 d)
.D E 4 ;:l
Z 2
0 2 4 6 8 10 12 14
12 1 .- T 1 r ----,-
10 Dead Only
VJ d)
·u 8 d)
0.. f/)
...... 6 0 ....
U .D 4 6 ;:! Z 2
q,
0 .1. -L ---L.
0 2 4 6 8 10 12 14
Anclote Ri er Kilometer
igure 9: Sp cie richnes by ri ver kilomet r for intertidal and ubtidal material combined .
16
Robbin. horeline Mapping
Number of lnd i idual 2 - Live and Dead per m
'" ,.... 800 - -. ---, T- T c: .....
ubtidal and Lntertidal (!)
0-en ~
600 :l
-0
: ~ 400 "0 c:
4-0 ..... 200 (!) .0
5 :l Z
0 2 4 6 8 10 12 14 N 800 T T -.-- -, 8 .....
Intertidal Only 11)
0-en 600 ~ :l
"0 .;; 400 "0
c: ,...., 4-0 ..... 200 11)
.0 5 :l Z 0
0 2 4 6 8 10 12 14
N 800 T T ~ ~ -r E .... Subtidal Only (!)
0-en 600 ~ :l
-0 > 400 "0 .s
4-0 ..... 200 (!) .0
E 'i'. :l Z 0
0 2 4 6 8 10 12 14
Anclote River Kilometer Figure 10: aunal densi t by ri er kilometer for Ii e and dead material combined.
17
Robbin" horelin Mappmg
umber of lndi id ual 2 - Subtidal and Intertida l per m
N 800 -.- ---, E .....
Live and Dead ~ 0. f/]
"i 600
::I "0
> 400 J "0 c:
4-0 ..... v
.0 6 ::I
Z 0 ---L
0 2 4 6 8 10 12 14 N 800 - ..
6 b Live Only 0.. U')
"i 600
::I "0
: ~ 400 "0 c: ...... 4-0 ..... 200 0
.0 E :J
;Z 0 0 2 4 6 8 10 12 14
N r
800 1 r ::: ..... Dead Ont_ o 0. (JJ
"i 600
::I "0 .>
400 "0 ::: -..
4-0 ..... 200 0
.0 E ;:s ~
Z 0 0 2 4 6 8 10 12 14
An lo te Ri er Kilom ter
Figure 11: aunal den it by ri ver kilomet r r int rtidal and ubtidal materi al combined.
Robbins horeline Mapping
40 ~------------------------------------------------------~
~ -~ 30 0-
W "o ....
Q)
.D E 20 ;l
:z Q)
> ~ :l 6
U 10
/
../'
,; ,;
,;
_/
/ /
~-----_-/
/ , .- - -/
/ ./ __ 1./
--/" J
/
/
O~--r-----.-----.------r-----'------r-----.-----.-~
o 2 4 6 10 12 14
River Kilometer (Progre sing Up tream)
4
V) Q) '\ -0 0 '\ Q) 0-
C/J "-0 .... 0.1
.D § 20 -' :z Q)
-f ~ ;::l 10 ~
0
----,~ ,_. \..
0
0 2 4 6 10 12 14
Ri er Kilometer (Progre sing Downstream)
olal - _ . - - h1tertida l -- - --- ubtidal
Figure 12: Cumulati e P Cle richne s by river kilometer.
19
Robbin horeline Mappmg
Exhibits
If.
20
Robbin: horeline Mapping
Anodontia alba • Li e 0 Dead
Intertidal Subtidal 20
1 1 J 18 • 0 N 16 E: L.. 14 Q) 12 0-L.. 10 Q)
8 o . 0 .Ll E 6
L, :::l 4 Z 2 0 T
1 0
50 ,.-.. 40 E: E 30 '-" 0 Q)
20
1 • l en
10 o ·
0 T
100
1 a 1 '" ~ 80 t: Q)
> 60 :l .....,
J ...
40
1 § u t 20
0..
0 ..J. ~ . ~ --e
10
x 8 0
i v 0 '"0 t: 6 0 ..... ~
-5 4 1 to
J ft. V
~ 2 • • 0
0 5 10 15 0 5 10 15
R.i er Kilomet r
21
Robbins horeline Mapping
Anomia implex • Li e 0 Dead
lnt rtidal ubtidal 10
N 8 0 0 10 0
E ....
I ~ 6 0-....
1 ~
4 0 0 ..0 E ;::l
2 ;z:
0 T T --,.-l 1
50 f ..-, 40 1=
E 30 '-"
i 0
~ N 20 ..... en 0 0
10 0 0
0 ,- T T r
100 1 en ~
·2 80 ~ ;> 60 ;::l -, ....
40 c ~ u &3 20
0...
0 1 , e --r- ,- e ~-e T -B-
10
j x 8 0 ~
"0 0 ro
~ ~ .::l 0 0 ~
-5 co
0 if. ~
~
,- -- T
0 5 10 15 0 5 10 15
Ri er Kil m ter
22
Robbtn boreline Mapping
Chione cancellata • Live 0 Dead
60 Intertidal Subtidal
N 50 0 E 0 b 40 P- o ~ 30 cu 0 ~ 20 t:: • :l Z 10 •
0 ,- T T - T --r
20
~ 15 0 ,.-.. • 0
§ 0 --' 10 • cu 0 0
i:I3 5
0 ,- 1--- r T ,--
100 1 • l 0
Vl cu t:: 80
0 cu > 60 :l -, • ......
40 t:: cu 0 U
1 j ....
20 cu 0-
0 -e I T 9 -----,- T
10 ;>( 8 cu
-0 t:: 6 - 0 ~
00 cu 0 I ...c: 4 ......
~ C\)
'f. 0)
0 ~ 2 1 • • 0 . T- ----,'
0 5 10 15 0 5 10 15
River Kilometer
Robbin h reline Mapping
Crepidula plana • Liv 0 Dead
Intertidal Subtidal 30
l N 25 0 8 ..... 20 (\)
0. 0 ..... 15 (\)
.D 10 E 1 0 00 ;:J
l, z 5 --l
0 -r- r T
20 ~
.-., 15 j § 00 00
10 0 '-' (\)
U5 5
0 T --r
100 . tI)
~ 80 c (\)
0 > 60 ;:J -. 0 .... 40 c
j Q) ()
~ 20 p,..
0 -e- ., T T
10
;< 8 Q)
'0 0 c 6 0 0 00 ,.....
~ ...c 4 .... ro
~ Q)
~ 2
o . ., 0 5 10 15 0 5 10 15
Ri er Ki lom teT
24
Robbins horeline Mapping
Laevicard;um morton; • L iv 0 Dead
80 intertidal ubtida l
N • E 60 ..... GJ 0.. ..... 40 GJ
..0 != • 0 ;3 20 • -;Z
ce 0 T r
20 -15 • ,-... i • § ~ «)
'-' 10 ~ eece (j) ,
U) 5
L-~ 0
100 • ] til (j)
5 80
> 60 0 0
::3
,J
......, +-'
40 ~ GJ • U .....
20 (j)
0... • 0 T r l
T - -«:)
10
>< 8 (j)
"0
-- 6 ..::: .....
0 (j)
..J:: 4 --i ~ 00 GJ ~
~ 2 c- o • --0 T T --,
0 5 10 15 0 5 10 15
Ri erKil met r
2
Robbins borel ine Mapping
Littorina irrorata • Li e 0 Dead
Intertidal Subtidal 100
j I N 80 • j E
.... Il) 60 0.
t 40 ~
1 •• • • E
:::I 20 • Z 0 0
0 T 1" r ----r T
40
j --- 30 E ••• o· E 0 '-' 20 Il) • N
C/l 10 ~ • 0 T ,-- T
100 r- 1 '" Il)
~ 80 -1
Il)
> 60 ~ 1 ..... ~ 40 Il) u
~ ....
20
J Il)
0.-
0 • e-r------ Q e ,-
10
r >< 8 Il) "0 0 ..5 6 ....
0 Il) ..c 4 -j .-
CI;I Il) • 'i'. ~ 2 • • • -0 r- -,-J
I
0 5 10 15 0 5 10 15
Ri er Ki lom ter
26
Robbin - hare line Mapping
Mulblia lateralis • Live 0 Dead
In! rtidal Subtidal 120
r N 100 0 E .... 80 <:)
0- • 0 .... 60 Il) 0 ..0 ... 40 t:: ::l
t z 20 l 0
0 1 T T T ~
20
1 15
1 • 0 § 0 0
'--' 10 0 Il)
CI} 5
o -'- ---r
100 '" Q)
t:: 80 -< Q)
>
60 i ::l ,...., 0 +-' 40 t::
Q) u
J ....
20 Q) 0 Cl.
0 1 · -e G
10
>< 8 Il)
" t:: 6 0 .... 0 Il)
0 -5 4 . ~
0 Q)
1 ~ ~ 2 1 • 0 1
0 5 10 15 0 5 10 15
Ri er Kilometer
27
Robb111S - horeline Mapping
Nassarius vibex • Liv 0 Dead
I nteltidaJ ubtidal 40
1 N «)
E 30 ' I- 0 <1)
0-
j .... 20 <1) • .0 E 10 ~ •• Z
0 • 1 --r 20
--- 15
I E .~ E • '-" 10 0 <I) •
if.) 5 L 0 - r
100 -j • rn <I)
'2 80 <I)
> 60 ~
1 ...... 0 -r' 40
1 [) 0 (.)
5 20 Q..
0 1 •• ----e 1
10 1 ><: 8 G)
"0 ..s 6 I '-
1 Q) .... 4 0 +J ro
0 t;, <I)
3 2 ••• • 0 T I
0 5 10 15 0 5 10 15
Rj er Kil m ter
28
Robbin.. boreline Mapping
Tel/ina tampaensis • Live 0 Dead
Intertidal ubtid I 40
J 0 E 30 -1 .... v 0.
1 .... 20 v -•
j ..0
§ 10 • ;z: • «)
0 I T r - --,
14 12
0 •
,-.. 10 • § •• 8 '--" v 6
. ~ C/} 4 0
til 2 o 1. T-
100 { - • til V
c 80 v ;> 60 -1 = ....., • .-
40 c v 0 <.) .... 20 ~ <.)
0... ,J o - T O r • e- 1
10
1 1 >< 8 I!) "'0 0 .s 6 0
i' .... v
0 -£i 4 ro v a: 2 - • -o - 1 -, 0 5 10 15 0 5 10 15
River Kilom ter
29
Robbin horeline Mapping
Part Two: horeline Mapping
A "wind hield" u e of the Anclol River to identify change !break in horeline typ a conducted during January 2006. The urvey \Va condu ted from a small boat. All
horeline as ociated with the main channel ( igur I) of the ri er including island and ba ou horeline were included in th urvey. hange !break in horeline type were patially regi tered using a W AA -enabled GP and phot graph d digitall . Logi ti
con traint ( .g. awyer and I gjam) ociated with the river' narro phy iognom up tream ofRKI re tri ted the urv to area below RK20.
Field data were used to create a GI hapefi le depicting the ri er' horeline with segment d fined b typ (e.g. mangro e) u ing the appropriate FLU cod (Table - 4). Segment defin iti ns were de eloped to repre ent a minimum of 9 % of the visible horeline as e n from th urv boat - for example, medium den ity re idential area
with singl story uni ts (12 1 I) with a narro\ fringe of mangro e tre ar defined a 12 11 n t a mangro e swamp (612).
ach horeline egment was cia sifi ed at F Level I through 4 a depicted in igures 2 through S wi th clas ification ba ed on a compilation of the urvey data and
data (e.g. horeline position) extra ted from the Oi trict 2004 ( I :24000) natural color aerial photograph . After completing this exercise, the ri er wa split into additional egments defined b river ki lometer and shoreline po ilion ( orth or outh) (Figure 6)
using data provided by the District (Figure 7). Till shapefil e w u ed to categoriz each horeline egment b river ki lom t rand horeline p ition (Figure 8). ote that ri er
kilometer polygons are not of equal ize because of the si nuo ity of the river. Thi caveat i al true for the amount of horelin contained in th mailer horeline po ition p I gon created (F igure 9). Difference in the proportion of shoreline by river ki lometer and horel ine positi on are illustrated in Figure 10.
FL Le el 1 (Wetland) i the dominant horeline cIa ification category wi th the rban and Bui1t- p (FLU I; Table 1) being e ondary. A ompari~ on of the e
categorie aero ri er kilometer i illustrated in Figure II . More pecifi c wetland categorie (FL S Level 2; Tabl 2) show large-scale break in hor line by cat gory (Figure J 2). TIll pattern doe not change wh n examining th horeline egment at the more specifi FL C S Level 3 or 4 cia ification (e.g. Figure I ). Le generalized
rban and Built- p categorie (FL Le el 2) how that the large t concen tration of high den ity urbanization can be found at RK5 and 6 (Figure 14 , indicati e of Tarpon Spring and it wharve with high-d n it hou ing extending fr III RK 1 t RK 15 (Figur 14).
The most peci fic cat gory used to cIa siry the river' horeline egment was FL Level 4 (Table 4) . From a remote en ing per p cti e till icon id r d a fairl high Ie of re olution (1 :6000) ' how er mapping at this level f re olution re ulted in orne ar a o fintere t not being identifi d in the h reline hapefil b eau e of their mall ize. For e 'ample, ju t above RK J 6 i a fTe h\ ater mar h fringe (Figure IS) that i < I m wide and no m re than 1 m in length. Ithough tIll i id ntifiable fr rn a b at , it doe meet
o
Robbins horel ine Mapping
the cri t ria of representi ng a minimum of90% of the visibl e shorelin a een from the urvey boat thu it i not repre ented in the horeline hapefi le. ther fr hwater wetland
are illustrated in Figure 16 through 18. Saltwater wetland including both fore ted and non-fore -ted are illu trated in Figure 19 till ugh 2 . ample of armored hor at
arying urban cia ifi ations are illu trated in Figure 24 through 28. Finally Figure 29 i an example of FL de 8 147 defined b thi -tud a a blidg ,
In addition to thi letter rep 11, the proj ct ' d liverable in lude 1) an containing horeline segment length, egrnent endpoi nt c ordinates. S ode, ri er kilomet r and other ancillary information ' 2) an Arc hapefile depi ting horeline cia ifi cation at ea h FL S level; 3) the 1999 FL C cia ification hapefil e; 4) the 2004 (I :24000) natural color aerial photograph . and 5) digital image of horeline de ignation .
Table I : Level I FLUCCS descriptions. Level 1 Attribute
I Urban and Built-Up 2 Agriculture 3 Rangeland 6 Wetlands 7 Barren Land 8 Transportation, Communications and Utilities
Table 2: Level 2 FLUCCS descriptions. Level 2 Attribute
1 1 Residential , Low Density 12 Residential, Medium Density 13 Residential , High Density 14 Commercial and Services 15 lodustrial 18 Recreational 19 Open Land 2 1 Cropland and Pastureland - -- -32 Shrub and Brushland 6 1 Wetland Hardwood Forests 63 Wetland Forested Mixed 64 Vegetated Non-Forested Wetlands 7 1 Beaches Other Than Swimming 74 Disturbed Land 8 1 Transportation 83 Utilities
.., I
ft,
Robbins - hore1ine Mapping
Table 3: Level 3 FLUCCS descriptions. Level 3 Attribute
1 J I Fixed Single Family Uni ts 11 3 Mixed Units 12 1 Fixed Single Family Uni ts 131 Fixed Single Family Units 133 Multiple Dwelling Units 145 Tourist Services 150 Industrial 155 Other Light lndustrial 159 Industrial Under Construction 181 Swimming Beach 182 Golf Course 186 Community Recreational Faciliti es 19J Undeveloped Land within Urban Areas 193 Urban Land in transition wi thout positi ve indicators of intended acti vity 194 Other Open Land 2 11 Improved Pasture 322 Coastal Scrub 6 12 Mangrove Swamps 630 Wetland Forested Mixed 642 Saltwater Marshes 710 Beaches Other Than Swimming Beaches 743 Spoi l Areas 744 FiU Areas 8 14 Roads and Highways 815 Port Facilities 83 1 Electric Power Facilities
If.
2
R bbill - horeline Mapping
Table 4: Level 4 FLUCCS descriptions. Level 3 Attribute IIII Single Story Units 111 2 Two of More Story Units 1130 Mixed Units 12 11 Single Story Units 1311 Single Story Units 1330 Multiple Dwell ing Units -.-1335 Townhouse Uni ts 1450 Tourist Services 1500 industrial 1550 Other Light Industrial 1590 Industrial Under Construction 18 10 Swimming Beach 1820 Golf Course 1860 Community Recreational Facilities 1910 _Undeveloped Land wi thin Urban Areas 1930 Urban Land in transition wi thout positive indicators of in tended acti vity 1940 Other Open Land -2 11 0 Improved Pa~ture 3220 Coastal Scrub 6 120 Mangrove Swamps 6300 Wetland Forested Mixed 6422 Needlerush 7100 Beaches O ther Than Swimming Beaches 7430 Spoil Areas 7440 Fill Areas 8147 Bridges 8150 Port Facilities 81 52 Piers 83 10 Electric Power Facil ities
'to
33
\I ~~ \ "- ' ,
Robbin - horeline Mapping
003507 l ' 21 28 kllome1er..::
Figur I : horeline depict ion delineated ITom the Oi triet' 2004 natural color aerial photograph ( I :24000).
34
FLUCCS LOY I I "
Ago II!
-- Barren
Ra eland
R bbiD. - boreline Mappio
Tr. onaDon, ComrronlC3oon and lJIIirtJes
- Urban and Buill-Up
ands
Figure 2: A depi ction of the Anclote Ri er FL L ell .
35
--o 0 35 07
\ ~l; , . ,,~
... , .. J ,
I ~ Kilometers
21
horeline with hor lin egment defined at
FLUCCS Lt vel 2
Be.ches Qh", Th s...m.ng
Conmerosl and S€Ivu:es
Oopland and Pasruretand
Qsl\Jfbed lind
Indu aI
-- ~en Land
rea .al
Re5fdenaal. HIQh~
Robbms
Reslder1laJ. Lo,,", Ot!rlsny
ResJde .... aI . Medun Oensny
Shrub and Brush land
Transportlllion
Ubillles
dan<! Forested MIXed
and H arrMwd Forests
o 035 0 7 21 2 8
boreline Mapping
Figure 3: A depiction of the Anclote Ri er h reli ne wi th shoreline segments defined at FL Le el 2.
6
Robbins - horeline Mapping
FlUCCS l •• 1 J Sea ches flf Than SW'Tfn ng Bea
Coastal Scrub
Corrrnurnty RemaDonai Fac.loes
8ec:trical Power Facilltes
RnAreas
R.<ed Smgle F arroly UnIts
Golf Course
l"ll"M'd Pasrure
tndustn.1 \~
p ~ '°0 ~ ~
()
If Umer Construrnon
'*'Pie o..eJhng UnIts
u gtt IndUSlJi3I
Open land
PDn Facilities
-- Roads and HIghways
SaI .... let ar'!tles
Spa. Area
s....m..gBeacn Taunst SeMces
~ed Land ""Ihon Uroan Areas
and land In translllon WlhOUl PO"""'"' .ndlcal!n of ""ended /ldJ1Iily
andF d M.xed
-00 350 7 14 21
""-..s 28
Figure 4 : A depiction of th Andote Ri er' shoreline with horelin egments defined at FL Level 3 .
37
FL UC CS LOIrel •
Beadles 0heI Than S\wrrtq Beaches
!hi91'S
Coastal Scrub
Coomunty ~ nal Fa es
8 edocaJ PowerFaci -
-- FiRAt".s
Golf C0t6Se
IlT"I'<oYed Pas1Ure
'"au ' at
Indu 81 Under Conscu:oon
Mangroves
Moced Uruts
M~le (Mel lJM:s
-- Needlerush unclJS
OIh<r gtot Indus:nal
-- Clller Open Land
PIers
Pon Faoll1leS
Sngle SlIl'Y Uno
Spo~ Are.l
s...TTYTlIng Bea
Tounst
TDMlhouse unllS
TWJ of Mote SIIJfy Unots. r....., or More Story lkJ
lkJde-.eJoped Land w lhon U!tIan Areas
lJrtJan Land III Iran lIOn ....:hoLt posi)"" IndlC310fS d lrulllled acn-..ty
WeIl and Forested M,xed
- -o OlS 07 1 . ~m~ers
2 1
Robbin - horeline Mappmg
2 8
Figure 5: A depi tion ofth An lote River's 'horeline with horeline segment defined at FL C Level 4.
3
003507 1 • Ki:tome1 ers
21
ob In - horeLille 1apping
28
Figur 6: An lot Ri er divi ion ba ed on ri er kilometer and horeline.
39
Robbin - horeline Mapping
•
o 0 35 0 1 4 21 28 omelets
igur 7: A repre entation of two hapefiles (centerline and ri er km) and their associated data provided by lhe Di triet.
40
Robbins horeline Mappmg
Rl . r Km a n d Shore Oulg n aUons
I S.mtl 3 S 6, e , South II SouIh
I Nonh 6, B, Non II , No
2 SouIh 4No - 9, South 12 Sou:n
1 Nonh 5 1, No h 10, North 12 orth
rth 5 nh B, North 10,SotJt> 13 N
13, South 16, North 18 SouIh
1~ , South I , S.mtl 19
14, 1 0'111 I7,SotJt> IB, So&.Ih
15, 17, North 111 . Norm 15, So.nh Ie, North
Figur : An la te Ri er sh reline egment clipped \ ith the hapefi le depicted in Figure 6.
4 1
14
12
10
C 8 (l)
~ (l)
CL 6
4
2
o
Robbin - Shorel ine Mapping
r-
r-
_ r-
r-
.-r-.-
r-
r- r-
.-r- r-
r- .-
nn ~ n
1 2 3 4 5 6 7 8 9 1 0 11 1 2 13 14 15 16 17 18 19 20
River Kilometer
Figure 9: Di tribution 0 horeline length brier IUlometer.
42
16
14
12
10 ..... c Q) (.) 8 ..... Q)
a.. 6
4
Robbm horeline Mapping
_ North Shore
r:=:J South Shore
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20
River Kilometer
Figure 10: Oi tribution of hor lin length brier kilometer and hare designati o.
ft.
4
14
12
10
C 8 Q)
~ Q)
a.. 6
4
2
o
Robbins - horeHne Mapping
_ Urban and Built-Up c=J Wetlands
Jl~ ll ~ ~ Jl . I I I I I J -- • 2 3 4 5 6 7 8 9 1 0 11 12 1314 15 16 17 18 19 20
River Kilometer
igure I 1: Di tribution of major h reline type (FLU Le II).
44
Robbin - horeline Mapping
1 4 .-------------------------------------------------~
12
10
C 8 Q) o .... Q)
a... 6
4
2
_ Wetland Hardwood Forests Wetland Forested Mixed
c:=J Vegetated Non-Forested Wetlands
2 3 4 5 6 7 8 9 1 0 11 12 13 14 15 16 1 7 18 19 20
River Ki lometer
Figure 12: Di tribution f wetland by type (FL Le el2).
45
'i'.
Robbins - Shoreline Mappmg
14
J _ Mangrove Swamps Wetland Forested Mixed Saltwater Marshes
10
..... 8 c Q) U L-Q)
a.. 6
4
2
o I. , . , - , . , . ,-- . , ' - 10 · i r - I ' - ,I' - I f -y '7' ''T' -r.r "," ",' '/' I·,! ' ,' 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20
River Kilometer
Figure 13: Distribution of wetl ands (FLUCCS Level 3) by river kilometer.
5>
46
Robbins - Shoreline Mapping
3.0
Low Density 2.5 -l n CJ Medium Density
c=J High Density Commercial
2.0 -j II ~ Industrial _ Recreational
C I I _ Open Land
(!) (.) 1.5 .... (!) a..
1.0
0.5
0.0 "I If l t • II I , .-! I , . " .". . II lI t · · til · I!, II . 11 , . II I · "i I I, II " i II !II II "I · pi
2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20
River Kilometer
Figllre 14 : Distribution of urban areas (FLUCCS Level 2) by fiver ki lometer.
~
47
Robbin - horeline Mappmg
Figure 1 : An e ample ofa small freshwater marsh fringe fronting a tand of mixed hardwood and palm at RK 16.
4
Robbins horeline Mapping
Figure 16: An example of the natural shoreline and narrow waterway with its inherent awyers and logjams above river km 18.
49
Robbins - Sborelme tapping
Figure 17: An example of giant leath r fern growing along a natural shoreline. Th.i freshwater wetland, located between RK 17 and RK 18, i too small to be delineated in Level 4 shapefile.
50
Robbins - ShoreJjne Mapping
Figure 18: A typical unannored boreline cia sified as FLU S Level 4, Wetland Fore ted Mixed.
51
Robbin - Shorelme 1apping
Figure 19: altwater marsh with a ingJe mangro ve apling at about RK 12.
52
Robbins - horeline Mapping
Figure 20: A Brazilian pepper growing along the 'outhem bank of the river above RK1 3.
R bbins horeline Mapping
Figure 21 : A natural horeline b rdering a ingle-family dwelling (FL S code 11 11 ).
4
Robbin - horeJjne tapping
iglW 22: An example o f a lightl modified mangrove dominated shoreline. ole the debri or rubble u ed t armor th horeline.
55
Robbin horeline Mapping
Figure 2 alt at r mar h fling (Juncu pp.) \ ith mangro e eed ling at RK I I.
5
Robbin ' - boreline Mapping
Figure 24: olf courue located on the northem bank at RK 12 with rubble u ed to annor the horeline.
7
Robbin ' - boreline Mapping
igure 25 : An example of ne\ on truction with rubble u ed to annor th shoreline at RKIS .
5
Robbins horeline Mapping
Figur 26: An armored horeline with do k and a mall tand of T pha pp. at RK 17.
59
R bbin · horelin Mapping
Figure 27: Tv 0 ample of concret wall used to armor tlle shoreline.
60
Robbins horeline Mapping
Figure 2 : An ample of an older horeline ann nng trateg .
6 1
Robbins - horeline Mapping
Figure 29: An e ampl of FL code ]47 at RKI6 defined b thj tudy (Table 4).
62