resp resp element_global_id elcode_bcd

Canada Canada 783947 CEGL002788

Canada 786781 CEGL002824

Canada 686311 CEGL003355

Canada 787986 CEGL002846

Canada 787997 CEGL002848

Canada 786787 CEGL002826

Northeast 687352 CEGL006013

Northeast 758559 CEGL006209

Northeast 683465 CEGL006043

Northeast 685788 CEGL006003

Northeast 687104 CEGL006376

Northeast 687976 CEGL006223

Northeast 687176 CEGL003766

Northeast 687798 CEGL006108

Northeast 801805 CEGL006587

Northeast 688955 CEGL006157

Northeast 689833 CEGL006388

Northeast 688078 CEGL006022

Northeast 689830 CEGL006052

Northeast 684064 CEGL006319

Northeast 758662 CEGL006218

Northeast 689488 CEGL007748

Midwest 683276 CEGL000383

Midwest 688207 CEGL005119

Midwest 683930 CEGL002095

Midwest 684146 CEGL002134

Midwest 684332 CEGL002140

Midwest 684876 CEGL002052

Midwest 686656 CEGL000554

Midwest 683906 CEGL004217

Southeast 688505 CEGL007386

Southeast 687447 CEGL006308

Southeast 684253 CEGL006049

Southeast 685533 CEGL004671

Southeast 687375 CEGL002319

Southeast 684482 CEGL004548

Southeast 689168 CEGL004420

Southeast 683496 CEGL007055

Southeast 689010 CEGL004553

Southeast 684918 CEGL007003

Southeast 689950 CEGL007316

Southeast 685717 CEGL007005

Southeast 685498 CEGL007282

Southeast 686057 CEGL007752

Southeast 685907 CEGL007057

Southeast 686930 CEGL007058

Southeast 687339 CEGL003506

Southeast 688412 CEGL007384

Southeast 688254 CEGL002054

Southeast 688053 CEGL007458

Southeast 688744 CEGL004963
Southeast 687993 CEGL006246

Southeast 684081 CEGL006130

Southeast 685121 CEGL007001

Southeast 683479 CEGL007002

Southeast 689616 CEGL004483

Southeast 689214 CEGL004436

Southeast 686218 CEGL004437

Southeast 684467 CEGL007166

Southeast 686636 CEGL004481

Southeast 688666 CEGL008577

Southeast 686144 CEGL007015

Southeast 687610 CEGL007016

Southeast 684472 CEGL003503

Southeast 685115 CEGL004712

Southeast 684814 CEGL003735

Southeast 686514 CEGL004550

Southeast 783931 CEGL004116

Southeast 684821 CEGL004635

Southeast 689430 CEGL007130

Southeast 685035 CEGL004983

Southeast 683985 CEGL007128

Southeast 689187 CEGL004942

Southeast 683912 CEGL003553

Southeast 688836 CEGL004668

Southeast 686193 CEGL003555

Southeast 720797 CEGL004053

Southeast 687597 CEGL007800

Southeast 689092 CEGL004447

Southeast 689963 CEGL007815

Southeast 688090 CEGL003532

Southeast 687831 CEGL003533

Southeast 686829 CEGL003538

Southeast 685316 CEGL004534

Southeast 685530 CEGL004792

Southeast 688011 CEGL007738

Southeast 687382 CEGL007513

Southeast 732730 CEGL004085

Southeast 686766 CEGL003608

Southeast 684152 CEGL004790

Southeast 688924 CEGL004497

Southeast 688937 CEGL003660

Southeast 687302 CEGL004499

Southeast 688223 CEGL004500

Southeast 688406 CEGL003661

Southeast 687752 CEGL004502

Southeast 687891 CEGL003663

Southeast 683711 CEGL003664

Southeast 684030 CEGL004495

Southeast 689074 CEGL004496

Southeast 688120 CEGL004945

Southeast 685092 CEGL003580

Southeast 689477 CEGL004957
Southeast 687903 CEGL004491

Southeast 687535 CEGL003592

Southeast 683890 CEGL007767

Southeast 689458 CEGL003596

Southeast 684980 CEGL003597

Southeast 732797 CEGL004086

Southeast 686870 CEGL003654

Southeast 686815 CEGL003573

Southeast 687946 CEGL003768

Southeast 686593 CEGL004968

Southeast 688441 CEGL004433

Southeast 687357 CEGL007721

Southeast 721877 CEGL004069

Southeast 685930 CEGL003721

Southeast 721871 CEGL004068

Southeast 686817 CEGL003722

Southeast 689799 CEGL002433

Southeast 684358 CEGL007296

Southeast 683518 CEGL004422

Southeast 684375 CEGL007540

Southeast 689980 CEGL007060

Southeast 686309 CEGL004975

Southeast 687012 CEGL003758

Southeast 685988 CEGL007405

Southeast 685314 CEGL007215

Southeast 683390 CEGL007775

Southeast 684592 CEGL007194

Southeast 688156 CEGL007272

Southeast 683919 CEGL007360

Southeast 688114 CEGL007256

Southeast 689466 CEGL003558

Southeast 683567 CEGL003711

Southeast 686865 CEGL007868

Southeast 721865 CEGL004064

Southeast 686580 CEGL007777

Southeast 689498 CEGL007467

Southeast 687755 CEGL003750

Southeast 689279 CEGL007851

Southeast 688019 CEGL007850

Southeast 689480 CEGL007454

Southeast 685008 CEGL007455

Southeast 689022 CEGL007011

Southeast 688325 CEGL003796

Southeast 685193 CEGL007004

Southeast 687309 CEGL004710

Southeast 685447 CEGL007725

Southeast 689084 CEGL004914

Southeast 684595 CEGL004424

Southeast 689536 CEGL004465

Southeast 684586 CEGL004653

Southeast 685925 CEGL004655

Southeast 687330 CEGL004711
Southeast 688765 CEGL008426

Southeast 686552 CEGL008513

Southeast 686534 CEGL004767

Southeast 687172 CEGL007138

Southeast 686418 CEGL007778

West 686147 CEGL000049

West 687574 CEGL000053

West 683744 CEGL000038

West 689112 CEGL001104

West 686296 CEGL000312

West 683983 CEGL003444

West 688516 CEGL008016

West 686038 CEGL008017

West 686463 CEGL008018

West 687718 CEGL008019

West 683924 CEGL008024

West 686181 CEGL000936

West 686031 CEGL000632

West 689088 CEGL000633

West 686378 CEGL000634

West 687383 CEGL000635

West 685642 CEGL000636

West 687679 CEGL002600

West 686961 CEGL000008

West 685443 CEGL000002

West 684647 CEGL000792

West 688266 CEGL000963

West 685584 CEGL000054

West 687481 CEGL000044

West 683385 CEGL000045

West 689308 CEGL000046

West 688445 CEGL003443

West 684197 CEGL000048

West 689692 CEGL008037

West 684906 CEGL008038

West 684769 CEGL008025

West 688912 CEGL003365

West 689160 CEGL008031

West 688309 CEGL008044

West 685090 CEGL002603

West 687648 CEGL003260

West 686505 CEGL002682

West 688683 CEGL002605

West 688948 CEGL000152

West 688194 CEGL000150

West 687065 CEGL000770

West 687785 CEGL000772

West 687221 CEGL000800

West 686673 CEGL000814

West 685396 CEGL000065

West 683092 CEGL003360

West 689097 CEGL000880
West 683120 CEGL000062

West 686747 CEGL000179

West 685390 CEGL000847

West 686362 CEGL003348

West 689096 CEGL000879

West 686824 CEGL000196

West 683636 CEGL000202

West 684301 CEGL003076

West 686064 CEGL003078

West 686929 CEGL008045

West 683405 CEGL000655

West 684665 CEGL003361

West 685184 CEGL000671

West 683956 CEGL003408

West 684059 CEGL000673

West 686980 CEGL000676

West 687636 CEGL000563

West 686301 CEGL001149

West 687463 CEGL008012

West 684055 CEGL008013

West 683825 CEGL008014

West 687530 CEGL008046

West 685236 CEGL008033

West 683597 CEGL008034

West 685704 CEGL008035

West 687119 CEGL003350

West 689819 CEGL000422

West 685358 CEGL000896

West 687475 CEGL000460

West 683251 CEGL000688

West 689012 CEGL000549

West 689013 CEGL000550

West 683302 CEGL000551

West 688184 CEGL000552

West 689592 CEGL003354

West 684009 CEGL000950

West 685553 CEGL008015

West 687888 CEGL008021

West 689671 CEGL000468

West 687058 CEGL000475

West 688913 CEGL003417

West 687402 CEGL000477

West 686131 CEGL000111

Canada 783950 CEGL002789

Canada 786776 CEGL002823

Canada 783944 CEGL002780

Canada 787981 CEGL002845

Canada 787585 CEGL002828

Canada 735931 CEGL002321

Canada 783962 CEGL002792

Canada 788002 CEGL002849

Canada 787597 CEGL002832
Canada 787973 CEGL002843

Canada 787600 CEGL002833

Canada 787594 CEGL002831

Canada 783966 CEGL002793

Canada 787608 CEGL002834

Canada 787611 CEGL002835

Canada 787617 CEGL002837

Canada 787591 CEGL002830

Northeast Northeast 800146 CEGL006592

Northeast 800143 CEGL006591

Northeast 687899 CEGL006413

Northeast 683445 CEGL006165

Northeast 736386 CEGL006262

Northeast 683137 CEGL006355

Northeast 688334 CEGL006002

Northeast 684706 CEGL006180

Northeast 689256 CEGL006212

Northeast 685562 CEGL006277

Northeast 800140 CEGL006590

Northeast 800184 CEGL006588

Northeast 800149 CEGL006593

Northeast 686109 CEGL006383

Northeast 790988 CEGL006329

Northeast 688606 CEGL006154

Northeast 687760 CEGL006117

Northeast 688343 CEGL006051

Northeast 686217 CEGL006384

Northeast 683533 CEGL006025

Northeast 685733 CEGL006203

Northeast 687664 CEGL006004

Northeast 685335 CEGL006040

Northeast 795520 CEGL006476

Northeast 742058 CEGL006901

Northeast 684643 CEGL006145

Northeast 689734 CEGL006030

Northeast 802102 CEGL006474

Midwest 689778 CEGL002079

Midwest 687870 CEGL002128

Midwest 687841 CEGL005173

Midwest 685222 CEGL005013

Midwest 689083 CEGL005014

Midwest 689876 CEGL000643

Midwest 689089 CEGL005232

Midwest 687009 CEGL000382

Midwest 688962 CEGL002057

Midwest 689376 CEGL005126

Midwest 685183 CEGL002402

Midwest 686787 CEGL002378

Midwest 688275 CEGL002111

Midwest 686124 CEGL001454

Midwest 687121 CEGL000660

Midwest 685460 CEGL002150
Midwest 684806 CEGL005054

Midwest 683064 CEGL002053

Midwest 687579 CEGL002137

Midwest 689584 CEGL000555

Midwest 689586 CEGL002145

Midwest 686638 CEGL002101

Midwest 685467 CEGL005037

Midwest 689285 CEGL002100

Midwest 683246 CEGL002417

Midwest 685462 CEGL002149

Midwest 686187 CEGL002405

Midwest 687178 CEGL002450

Midwest 686389 CEGL002596

Midwest 687168 CEGL002597

Southeast 687615 CEGL008566

Southeast 684542 CEGL007907

Southeast 688936 CEGL003659

Southeast 689404 CEGL007811

Southeast 685681 CEGL004931

Southeast 683222 CEGL004547

Southeast 686662 CEGL004551

Southeast 686637 CEGL007822

Southeast 684165 CEGL004425

Southeast 686554 CEGL003737

Southeast 689412 CEGL004781

Southeast 689831 CEGL007617

Southeast 685010 CEGL004504

Southeast 684667 CEGL004982

Southeast 685747 CEGL006124

Southeast 689218 CEGL008504

Southeast 689545 CEGL003752

Southeast 690039 CEGL004995

Southeast 683233 CEGL004747

Southeast 686672 CEGL008547

Southeast 686947 CEGL007563

Southeast 688311 CEGL007145

Southeast 685822 CEGL008598

Southeast 685755 CEGL003634

Southeast 688121 CEGL007151

Southeast 688673 CEGL006146

Southeast 689067 CEGL003505

Southeast 687549 CEGL004639

Southeast 689611 CEGL007783

Southeast 684324 CEGL007872

Southeast 683549 CEGL004965

Southeast 689589 CEGL007459

Southeast 688154 CEGL008554

Southeast 689482 CEGL004977

Southeast 721881 CEGL004072

Southeast 688985 CEGL007207

Southeast 684280 CEGL004539

Southeast 684450 CEGL003683
Southeast 689960 CEGL003684

Southeast 687942 CEGL007180

Southeast 683816 CEGL004478

Southeast 689340 CEGL004753

Southeast 689129 CEGL007926

Southeast 689346 CEGL004694

Southeast 687603 CEGL007728

Southeast 688138 CEGL007994

Southeast 689553 CEGL004410

Southeast 689880 CEGL002125

Southeast 687829 CEGL007833

Southeast 688224 CEGL004672

Southeast 684105 CEGL003525

Southeast 688183 CEGL007747

Southeast 683778 CEGL004271

Southeast 685911 CEGL007848

Southeast 689654 CEGL007779

Southeast 683170 CEGL007473

Southeast 683443 CEGL007047

Southeast 685327 CEGL007008

Southeast 690071 CEGL007007

Southeast 684512 CEGL004427

Southeast 686497 CEGL004428

Southeast 685828 CEGL007873

Southeast 688725 CEGL004679

Southeast 686626 CEGL008477

Southeast 684845 CEGL004684

Southeast 689696 CEGL004683

Southeast 683096 CEGL004720

Southeast 685341 CEGL004718

Southeast 686939 CEGL004641

Southeast 683834 CEGL007131

Southeast 687776 CEGL006256

Southeast 686886 CEGL006152

Southeast 685028 CEGL008501

Southeast 684173 CEGL004600

Southeast 686999 CEGL004596

Southeast 684459 CEGL004597

Southeast 689939 CEGL004598

Southeast 688440 CEGL003551

Southeast 684182 CEGL004599

Southeast 688714 CEGL007074

Southeast 689124 CEGL003554

Southeast 686240 CEGL003556

Southeast 684134 CEGL008492

Southeast 684143 CEGL004713

Southeast 684319 CEGL007507

Southeast 730941 CEGL003868

Southeast 683346 CEGL003855

Southeast 686515 CEGL004446

Southeast 685025 CEGL004445

Southeast 683060 CEGL002393
Southeast 684269 CEGL003559

Southeast 689079 CEGL008556

Southeast 687060 CEGL003650

Southeast 689594 CEGL003534

Southeast 685361 CEGL003535

Southeast 683910 CEGL004658

Southeast 684562 CEGL003673

Southeast 684401 CEGL007556

Southeast 687780 CEGL004969

Southeast 690066 CEGL004556

Southeast 689903 CEGL003638

Southeast 684147 CEGL004676

Southeast 685276 CEGL007750

Southeast 688772 CEGL004967

Southeast 683713 CEGL003647

Southeast 688494 CEGL008571

Southeast 689687 CEGL004774

Southeast 689504 CEGL008437

Southeast 687094 CEGL003662

Southeast 687904 CEGL004501

Southeast 683143 CEGL003577

Southeast 684626 CEGL008579

Southeast 689842 CEGL003569

Southeast 689843 CEGL003570

Southeast 689119 CEGL003646

Southeast 687061 CEGL003649

Southeast 684921 CEGL008586

Southeast 685254 CEGL008569

Southeast 687536 CEGL003602

Southeast 687194 CEGL007842

Southeast 685026 CEGL004487

Southeast 688272 CEGL003578

Southeast 683637 CEGL008572

Southeast 689621 CEGL003593

Southeast 688575 CEGL003589

Southeast 684185 CEGL007844

Southeast 688578 CEGL003590

Southeast 685300 CEGL003584

Southeast 685967 CEGL004488

Southeast 686414 CEGL003601

Southeast 688222 CEGL004490

Southeast 683754 CEGL003588

Southeast 732722 CEGL004083

Southeast 688221 CEGL004489

Southeast 683169 CEGL003595

Southeast 685091 CEGL003579

Southeast 684627 CEGL008580

Southeast 686767 CEGL003598

Southeast 687267 CEGL003599

Southeast 732726 CEGL004084

Southeast 685275 CEGL007749

Southeast 683119 CEGL007802
Southeast 685441 CEGL004955

Southeast 684289 CEGL003571

Southeast 688760 CEGL004956

Southeast 688597 CEGL003572

Southeast 686504 CEGL003581

Southeast 687545 CEGL003653

Southeast 689676 CEGL004486

Southeast 685965 CEGL007091

Southeast 689432 CEGL002124

Southeast 685914 CEGL004585

Southeast 686044 CEGL004985

Southeast 688822 CEGL003617

Southeast 684815 CEGL004434

Southeast 685002 CEGL003795

Southeast 683768 CEGL004652

Southeast 687406 CEGL003669

Southeast 688245 CEGL003797

Southeast 684257 CEGL007100

Southeast 685613 CEGL007524

Southeast 689896 CEGL007558

Southeast 688542 CEGL004651

Southeast 687982 CEGL003619

Southeast 685214 CEGL007548

Southeast 689688 CEGL003624

Southeast 686995 CEGL004691

Southeast 688303 CEGL007832

Southeast 685043 CEGL002132

Southeast 688480 CEGL004922

Southeast 721861 CEGL003880

Southeast 688264 CEGL004644

Southeast 683449 CEGL004541

Southeast 686440 CEGL007691

Southeast 685263 CEGL008581

Southeast 688475 CEGL004542

Southeast 689521 CEGL007773

Southeast 688065 CEGL008575

Southeast 689836 CEGL007295

Southeast 683530 CEGL003693

Southeast 683274 CEGL004912

Southeast 684381 CEGL007470

Southeast 688151 CEGL004412

Southeast 685469 CEGL004937

Southeast 686035 CEGL002117

Southeast 683680 CEGL007020

Southeast 688350 CEGL008599

Southeast 683681 CEGL007019

Southeast 689075 CEGL004506

Southeast 687515 CEGL003792

Southeast 686482 CEGL007023

Southeast 685138 CEGL007022

Southeast 687182 CEGL004787

Southeast 686304 CEGL002136
Southeast 683247 CEGL007472

Southeast 685596 CEGL007447

Southeast 686835 CEGL004421

Southeast 687561 CEGL004778

Southeast 683881 CEGL007549

Southeast 684585 CEGL004642

Southeast 689328 CEGL004756

Southeast 683408 CEGL007715

Southeast 689725 CEGL007449

Southeast 689740 CEGL007737

Southeast 814098 CEGL004267

Southeast 814348 CEGL004023

Southeast 688063 CEGL004927

Southeast 720781 CEGL003665

Southeast 732869 CEGL004092

Southeast 687508 CEGL007712

Southeast 688018 CEGL007849

Southeast 683704 CEGL007356

Southeast 683595 CEGL004643

Southeast 683458 CEGL007809

Southeast 686910 CEGL007364

Southeast 684588 CEGL007869

Southeast 685094 CEGL007403

Southeast 683611 CEGL004416

Southeast 687902 CEGL003706

Southeast 689678 CEGL007298

Southeast 689416 CEGL004503

Southeast 689862 CEGL008442

Southeast 686374 CEGL004709

Southeast 685990 CEGL004413

Southeast 687110 CEGL003714

Southeast 685712 CEGL003713

Southeast 683596 CEGL008587

Southeast 689425 CEGL003884

Southeast 684566 CEGL004670

Southeast 686780 CEGL003756

Southeast 689157 CEGL003712

Southeast 689138 CEGL004686

Southeast 685470 CEGL002156

Southeast 689777 CEGL003523

Southeast 687074 CEGL007032

Southeast 687576 CEGL002154

Southeast 686285 CEGL007466

Southeast 686284 CEGL004976

Southeast 687020 CEGL007026

Southeast 684469 CEGL007027

Southeast 687254 CEGL007476

Southeast 684976 CEGL002107

Southeast 684380 CEGL007469

Southeast 683678 CEGL007830

Southeast 689857 CEGL007028

Southeast 688005 CEGL007067
Southeast 689985 CEGL007053

Southeast 686314 CEGL002056

Southeast 689042 CEGL003526

Southeast 687469 CEGL004674

Southeast 689552 CEGL004409

Southeast 685672 CEGL007409

Southeast 688986 CEGL004423

Southeast 686307 CEGL004222

Southeast 687421 CEGL004587

Southeast 688322 CEGL003729

Southeast 688939 CEGL004981

Southeast 689126 CEGL007415

Southeast 688901 CEGL007414

Southeast 732872 CEGL004090

Southeast 688101 CEGL007416

Southeast 684162 CEGL003734

Southeast 687749 CEGL003733

Southeast 688203 CEGL003996

Southeast 686119 CEGL003997

Southeast 686969 CEGL004441

Southeast 685806 CEGL004681

Southeast 684897 CEGL003804

Southeast 687708 CEGL004682

Southeast 688741 CEGL004429

Southeast 687895 CEGL002104

Southeast 684718 CEGL007377

Southeast 688972 CEGL004654

Southeast 685765 CEGL007440

Southeast 687663 CEGL004231

Southeast 687507 CEGL008557

Southeast 686615 CEGL007711

Southeast 689336 CEGL007565

Southeast 687138 CEGL008533

Southeast 689569 CEGL007693

Southeast 684046 CEGL006178

Southeast 685244 CEGL007139

Southeast 689008 CEGL002388

West West 688736 CEGL000215

West 686608 CEGL000041

West 686330 CEGL000042

West 686148 CEGL000050

West 686702 CEGL000051

West 687218 CEGL000052

West 685602 CEGL000255

West 687436 CEGL000260

West 684070 CEGL000014

West 684819 CEGL000431

West 685297 CEGL000244

West 685060 CEGL000248

West 689440 CEGL000278

West 685023 CEGL002669

West 687581 CEGL000286
West 684035 CEGL000287

West 683070 CEGL000915

West 683583 CEGL000273

West 683320 CEGL000274

West 683833 CEGL000281

West 686621 CEGL000283

West 683467 CEGL000288

West 683145 CEGL000291

West 689276 CEGL000316

West 688449 CEGL000303

West 685220 CEGL003334

West 683184 CEGL000627

West 687613 CEGL000626

West 685384 CEGL000630

West 688391 CEGL000637

West 683536 CEGL001085

West 684006 CEGL000961

West 688393 CEGL000970

West 689805 CEGL000043

West 690027 CEGL000047

West 689377 CEGL000352

West 686781 CEGL000353

West 689174 CEGL003043

West 686632 CEGL003044

West 684452 CEGL003405

West 686558 CEGL003391

West 737495 CEGL005957

West 683360 CEGL002635

West 683248 CEGL000726

West 683155 CEGL000735

West 686022 CEGL000736

West 688653 CEGL000742

West 688363 CEGL000745

West 684938 CEGL000749

West 684939 CEGL000750

West 728669 CEGL005884

West 684797 CEGL000951

West 686714 CEGL008010

West 684015 CEGL000405

West 689108 CEGL000412

West 685783 CEGL000354

West 684794 CEGL000358

West 683934 CEGL000375

West 688583 CEGL000377

West 689353 CEGL002637

West 686077 CEGL000396

West 685674 CEGL000394

West 686922 CEGL000400

West 683705 CEGL000055

West 688232 CEGL003270

West 686486 CEGL000754

West 687333 CEGL000130
West 688238 CEGL000753

West 685793 CEGL000762

West 688328 CEGL000763

West 688064 CEGL003375

West 683648 CEGL000142

West 685038 CEGL000768

West 685748 CEGL000771

West 689547 CEGL000773

West 687448 CEGL000797

West 684970 CEGL000774

West 688112 CEGL000784

West 683069 CEGL000821

West 684032 CEGL003449

West 686489 CEGL003164

West 690091 CEGL000191

West 683982 CEGL000208

West 684313 CEGL000212

West 684242 CEGL000881

West 689762 CEGL000882

West 686597 CEGL000884

West 686468 CEGL000841

West 686681 CEGL002638

West 688333 CEGL000840

West 687934 CEGL000061

West 683660 CEGL000845

West 686748 CEGL000180

West 685719 CEGL000181

West 688785 CEGL000184

West 686718 CEGL000858

West 687498 CEGL000189

West 683981 CEGL000198

West 685480 CEGL000193

West 688843 CEGL000194

West 686825 CEGL000206

West 690073 CEGL002686

West 683800 CEGL000645

West 738779 CEGL005991

West 689057 CEGL002640

West 683572 CEGL000646

West 689020 CEGL000651

West 684936 CEGL000653

West 683422 CEGL002646

West 687134 CEGL000677

West 689415 CEGL000542

West 684232 CEGL003407

West 686073 CEGL000674

West 687707 CEGL003418

West 688724 CEGL000482

West 737581 CEGL005964

West 737568 CEGL005966

West 684220 CEGL000939

West 737595 CEGL005971
West 737969 CEGL005976

West 687845 CEGL002649

West 689191 CEGL000657

West 737959 CEGL005967

West 737972 CEGL005965

West 737586 CEGL005972

West 684223 CEGL000940

West 738786 CEGL005993

West 737592 CEGL005973

West 688559 CEGL000942

West 683532 CEGL000665

West 687971 CEGL002683

West 687093 CEGL002684

West 685892 CEGL000944

West 687653 CEGL000662

West 684946 CEGL000941

West 687363 CEGL001455

West 686353 CEGL000528

West 687698 CEGL000540

West 687046 CEGL000565

West 683642 CEGL003371

West 685678 CEGL000577

West 688104 CEGL000581

West 685862 CEGL000599

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Global Scientific Name

Picea sitchensis - Acer macrophyllum / Oplopanax horridus - Rubus spectabilis / Maianthemum dilatatum Forest

Picea sitchensis / Trisetum canescens Forest

Pseudotsuga menziesii - Quercus garryana / Melica subulata Forest

Thuja plicata - Acer macrophyllum - Abies grandis / (Oemleria cerasiformis) / Polystichum munitum Forest

Thuja plicata - Pseudotsuga menziesii - Abies grandis / Mahonia nervosa / Polystichum munitum Forest

Tsuga heterophylla - Picea sitchensis / Rubus spectabilis - Ribes bracteosum Forest

Acer rubrum - Nyssa sylvatica - Liquidambar styraciflua - Populus heterophylla Forest

Carya glabra - Quercus (rubra, prinus) - Fraxinus americana / Viburnum rafinesquianum / Piptochaetium avenaceum Forest

Fagus grandifolia / Smilax rotundifolia Forest

Fraxinus nigra - Abies balsamea / Rhamnus alnifolia Forest

Ilex opaca / Morella pensylvanica Forest

Liquidambar styraciflua - Acer rubrum - Nyssa biflora / Carex joorii Forest

Pinus resinosa - Quercus rubra / Sibbaldiopsis tridentata / Danthonia compressa - Antennaria virginica / Rhytidium rugosum Woodland

Pinus resinosa / Menziesia pilosa / Polypodium appalachianum Forest

Pinus rigida - Picea rubens / Viburnum nudum var. cassinoides / Sphagnum spp. Woodland

Pinus rigida - Quercus ilicifolia - Rhododendron canadense Woodland

Pinus rigida / Gaylussacia dumosa / Calamovilfa brevipilis Woodland

Pinus rigida / Vaccinium myrtilloides / Sphagnum spp. Woodland

Pinus taeda / Hudsonia tomentosa Woodland

Prunus serotina / Morella cerifera / Smilax rotundifolia Scrub Forest

Quercus bicolor - Fraxinus pennsylvanica - (Platanus occidentalis) / Chasmanthium latifolium - Dichanthelium clandestinum - Zizia aurea Woodland

Quercus muehlenbergii / Cercis canadensis / Dichanthelium boscii - Bromus pubescens - Erigeron pulchellus var. pulchellus - Aquilegia canadensis Forest

Picea glauca / Vaccinium scoparium Forest

Populus deltoides - (Juniperus virginiana) Dune Woodland

Populus deltoides - Platanus occidentalis Forest

Quercus alba - (Carya ovata) / Carex pensylvanica Glaciated Woodland

Quercus macrocarpa - Quercus bicolor - (Celtis occidentalis) Woodland

Quercus macrocarpa / Andropogon gerardii - Panicum virgatum Woodland

Quercus macrocarpa / Carex inops ssp. heliophila Woodland

Quercus stellata - Quercus alba - (Quercus falcata) / Schizachyrium scoparium Woodland

(Quercus laurifolia) / Crataegus opaca - Crataegus viridis Forest

Abies fraseri / (Rhododendron catawbiense, Rhododendron carolinianum) Forest

Abies fraseri / Viburnum lantanoides / Dryopteris campyloptera - Oxalis montana / Hylocomium splendens Forest

Acer barbatum - Aesculus glabra - Carya myristiciformis - Quercus shumardii - Quercus muehlenbergii Forest

Acer grandidentatum - (Quercus muehlenbergii) / Carex edwardsiana Lampasas Cutplain Forest

Acer grandidentatum - Quercus gravesii Forest

Acer rubrum var. trilobum - Fraxinus pennsylvanica / Carex crinita - Peltandra virginica Forest

Annona glabra / Crinum americanum - Bacopa caroliniana Forest

Arbutus xalapensis - Quercus grisea - Juniperus flaccida - Acer grandidentatum - Quercus gravesii Forest

Bursera simaruba - Swietenia mahagoni - Lysiloma latisiliquum / Nectandra coriacea - Coccoloba diversifolia Forest

Carya cordiformis - Quercus pagoda - Quercus shumardii - Carya myristiciformis / Sabal minor - Cornus asperifolia Forest

Casasia clusiifolia - Guapira discolor - Pithecellobium keyense - Metopium toxiferum / Solanum bahamense / Hymenocallis latifolia Forest

Celtis laevigata - Tilia americana var. caroliniana / Aesculus pavia Forest

Celtis laevigata - Ulmus crassifolia - (Fraxinus berlandieriana) / Rivina humilis - Chromolaena odorata Forest

Conocarpus erectus - Metopium toxiferum - Acoelorraphe wrightii / Chrysobalanus icaco Forest

Conocarpus erectus - Sideroxylon celastrinum - Erithalis fruticosa - Manilkara jaimiqui ssp. emarginata Forest

Conocarpus erectus / Sporobolus virginicus - Spartina spartinae Woodland

Cornus foemina / Berchemia scandens Forest

Ebenopsis ebano - Ehretia anacua / Condalia hookeri Forest

Fagus grandifolia - Magnolia grandiflora - Fraxinus americana / Acer barbatum - Cercis canadensis - Ostrya virginiana Forest

Fagus grandifolia - Magnolia grandiflora - Quercus pagoda - Acer barbatum - Pinus taeda Forest
Fagus grandifolia / Ageratina altissima var. roanensis Forest

Fagus grandifolia / Carex pensylvanica - Carex brunnescens Forest

Ficus aurea - Sideroxylon foetidissimum - Bursera simaruba / Eugenia foetida - Guapira discolor - Nectandra coriacea Forest

Ficus aurea - Sideroxylon foetidissimum - Bursera simaruba / Eugenia foetida - Piscidia piscipula / Hymenocallis latifolia Forest

Fraxinus pennsylvanica - Ulmus americana / Morella cerifera - Juniperus virginiana var. silicicola Forest

Fraxinus quadrangulata - Quercus macrocarpa - Quercus muehlenbergii / Arundinaria gigantea ssp. gigantea / Elymus spp. Woodland

Juglans nigra - Aesculus glabra var. glabra - Gymnocladus dioicus / Arundinaria gigantea ssp. gigantea - (Asimina triloba) Forest

Juniperus virginiana var. silicicola / Morella cerifera / Kosteletzkya virginica - Bacopa monnieri Woodland

Liquidambar styraciflua / Persea palustris Forest

Magnolia grandiflora / Prunus caroliniana - Carpinus caroliniana / Arundinaria gigantea Forest

Magnolia virginiana - Persea palustris - Chrysobalanus icaco / Acrostichum danaeifolium - Nephrolepis exaltata Forest

Magnolia virginiana - Persea palustris - Chrysobalanus icaco / Cladium mariscus ssp. jamaicense Woodland

Metopium toxiferum - Thrinax morrisii - Byrsonima lucida / Schizachyrium spp. Woodland

Nyssa aquatica / Cephalanthus occidentalis Pond Forest

Nyssa biflora - Taxodium ascendens / Ludwigia pilosa - Bacopa caroliniana Woodland

Nyssa biflora / Cephalanthus occidentalis - Leucothoe racemosa Forest

Nyssa biflora / Cephalanthus occidentalis - Lyonia lucida Sagpond Forest

Persea palustris / Morella cerifera Maritime Forest

Picea rubens - (Abies fraseri) / (Rhododendron catawbiense, Rhododendron maximum) Forest

Picea rubens - (Betula alleghaniensis, Aesculus flava) / Rhododendron (maximum, catawbiense) Forest

Picea rubens / Ribes glandulosum Forest

Pinus clausa - Quercus geminata - Quercus hemisphaerica / Quercus myrtifolia Forest

Pinus clausa / Ceratiola ericoides - Sabal etonia / Cladonia spp. Woodland

Pinus clausa / Ceratiola ericoides / Cladonia spp. Woodland

Pinus clausa / Quercus inopina Woodland

Pinus echinata - Quercus stellata - (Quercus marilandica) Forest

Pinus echinata - Quercus stellata - Quercus falcata - Carya texana Woodland

Pinus echinata - Quercus stellata - Quercus marilandica / Andropogon gyrans - Chrysopsis mariana Woodland

Pinus echinata / Schizachyrium scoparium - Solidago ulmifolia - Monarda russeliana - Echinacea pallida Woodland

Pinus elliottii var. densa / Coccothrinax argentata - Thrinax morrisii Woodland

Pinus elliottii var. densa / Sabal palmetto / Schizachyrium rhizomatum - Muhlenbergia filipes - Rhynchospora divergens Tropical Woodland

Pinus elliottii var. densa / Serenoa repens - Tetrazygia bicolor - Guettarda scabra Woodland

Pinus glabra - Quercus laurifolia / Crataegus opaca / Sabal minor Forest

Pinus palustris - (Pinus elliottii var. elliottii) / Ilex vomitoria / Muhlenbergia expansa - Agalinis filicaulis Woodland

Pinus palustris - (Pinus taeda) / Schizachyrium scoparium - Rhynchosia reniformis Woodland

Pinus palustris - Pinus (echinata, taeda) - Quercus (incana, margarettiae) / Schizachyrium scoparium Woodland

Pinus palustris - Pinus (serotina, taeda) / Sporobolus curtissii - Muhlenbergia expansa Woodland

Pinus palustris - Pinus echinata / Schizachyrium scoparium - Manfreda virginica Serpentine Woodland

Pinus palustris - Pinus elliottii var. elliottii / Ctenium aromaticum - Aristida beyrichiana - (Sporobolus floridanus) Woodland

Pinus palustris - Pinus elliottii var. elliottii / Styrax americanus / Sporobolus floridanus Woodland

Pinus palustris - Pinus serotina / Ctenium aromaticum - Muhlenbergia expansa - Rhynchospora latifolia Woodland

Pinus palustris - Pinus serotina / Ctenium aromaticum - Scleria pauciflora - Sarracenia flava Woodland

Pinus palustris - Pinus serotina / Magnolia virginiana / Sporobolus teretifolius - Carex striata Woodland

Pinus palustris - Pinus serotina / Pleea tenuifolia - Aristida stricta Woodland

Pinus palustris - Pinus serotina / Sporobolus pinetorum - Ctenium aromaticum - Eriocaulon decangulare var. decangulare Woodland

Pinus palustris - Pinus taeda - Pinus serotina / Chasmanthium laxum - Panicum virgatum Piedmont Woodland

Pinus palustris - Pinus taeda - Pinus serotina / Quercus marilandica / (Quercus pumila) / Aristida stricta Woodland

Pinus palustris / Arundinaria gigantea ssp. tecta - Liquidambar styraciflua / Andropogon glomeratus - Sarracenia minor Woodland

Pinus palustris / Clethra alnifolia - Gaylussacia frondosa - Quercus pumila / Schizachyrium scoparium Woodland

Pinus palustris / Quercus falcata / Cornus florida / Aristida beyrichiana Woodland

Pinus palustris / Quercus incana / Schizachyrium scoparium - Liatris elegans - Opuntia humifusa var. humifusa Woodland

Pinus palustris / Quercus incana / Sporobolus clandestinus Woodland
Pinus palustris / Quercus laevis - Quercus geminata / Ceratiola ericoides Woodland

Pinus palustris / Quercus laevis - Quercus incana / Gaylussacia dumosa - Gaylussacia (baccata, frondosa) Woodland

Pinus palustris / Quercus laevis / Leiophyllum buxifolium - Cyrilla racemiflora - Clethra alnifolia Woodland

Pinus palustris / Quercus marilandica / Schizachyrium scoparium - Silphium laciniatum - Ruellia humilis Woodland

Pinus palustris / Quercus marilandica / Schizachyrium tenerum - Muhlenbergia expansa - Bigelowia nuttallii - Packera obovata Woodland

Pinus palustris / Schizachyrium scoparium - Muhlenbergia expansa - Arnoglossum ovatum Woodland

Pinus palustris / Sporobolus silveanus - Muhlenbergia capillaris - Chaetopappa asteroides Woodland

Pinus palustris / Vaccinium elliottii - Clethra alnifolia / Aristida stricta - Panicum virgatum Woodland

Pinus rigida - Quercus alba / Sporobolus heterolepis - Andropogon gerardii Woodland

Pinus rigida - Quercus stellata / Andropogon gerardii - Packera paupercula Woodland

Pinus serotina / Arundinaria gigantea ssp. tecta Woodland

Pinus virginiana - Pinus rigida - Quercus stellata / Ceanothus americanus - Kalmia latifolia / Thalictrum revolutum Woodland

Quercus (rubra, alba, velutina) / Acer barbatum / Asimina triloba Forest

Quercus alba - Carya glabra / Schizachyrium scoparium - Helianthus divaricatus - Salvia urticifolia - Parthenium auriculatum Woodland

Quercus alba - Quercus falcata - Quercus velutina / Ostrya virginiana Forest

Quercus alba - Quercus velutina - Quercus stellata / Schizachyrium scoparium - Desmodium spp. Woodland

Quercus alba / Carex pensylvanica - Carex ouachitana Dwarf Forest

Quercus alba / Physocarpus opulifolius / Packera plattensis - Hexastylis arifolia var. ruthii Forest

Quercus bicolor - Fraxinus pennsylvanica / Carex spp. Forest

Quercus falcata - Pinus taeda - (Fagus grandifolia, Quercus nigra) / Persea palustris Maritime Forest

Quercus laurifolia - Sabal palmetto / Myrsine floridana - Psychotria nervosa Forest

Quercus lyrata / Betula nigra / Pleopeltis polypodioides ssp. michauxiana Forest

Quercus muehlenbergii - Carya carolinae-septentrionalis / Acer (barbatum, leucoderme) - Juniperus virginiana var. virginiana / Croton alabamensis Woodland

Quercus phellos - Quercus nigra - (Nyssa biflora) Forest

Quercus rubra - Quercus muehlenbergii / Hamamelis virginiana / Polymnia canadensis Forest

Quercus shumardii - Carya myristiciformis - (Quercus muehlenbergii) / Carex cherokeensis - Sorghastrum nutans Woodland

Quercus shumardii - Fraxinus americana - Carya myristiciformis / Viburnum dentatum / Carex cherokeensis Forest

Quercus shumardii - Quercus pagoda - Fraxinus americana / Ostrya virginiana - Cornus florida / Trillium ludovicianum Forest

Quercus similis - Quercus pagoda - Carya (glabra, myristiciformis, ovata) Temporarily Flooded Forest

Quercus sinuata var. sinuata - Fraxinus americana - Quercus muehlenbergii / Rhus aromatica - Cornus drummondii Forest

Quercus stellata - (Pinus echinata) / Schizachyrium scoparium - Echinacea laevigata - Oligoneuron album Woodland

Quercus stellata - (Pinus echinata) / Schizachyrium scoparium - Symphyotrichum georgianum Woodland

Quercus stellata - Carya texana - (Pinus palustris) / Chasmanthium sessiliflorum - Ranunculus fascicularis Woodland

Quercus stellata - Quercus falcata / Ostrya virginiana Forest

Quercus stellata / Forestiera ligustrina - Symphoricarpos orbiculatus / Carex cherokeensis - Schizachyrium scoparium Woodland

Quercus virginiana - Magnolia grandiflora - Quercus pagoda - Celtis laevigata / Sabal minor Forest

Quercus virginiana - Quercus incana Woodland

Quercus virginiana - Quercus nigra - Quercus pagoda - Liquidambar styraciflua / Sabal minor - Ilex vomitoria Forest

Quercus virginiana - Quercus pagoda - Magnolia grandiflora - Carya glabra / Ilex opaca Forest

Rhizophora mangle - Taxodium distichum - Metopium toxiferum / Chrysobalanus icaco / Apteria aphylla Forest

Roystonea elata - Taxodium distichum - Quercus laurifolia / Psychotria nervosa / Nephrolepis spp. Forest

Sabal palmetto - Coccoloba uvifera - Piscidia piscipula / Myrsine floridana / Hymenocallis latifolia Forest

Sabal palmetto / Serenoa repens Woodland

Sideroxylon foetidissimum - Sideroxylon salicifolium - Ficus aurea - Quercus virginiana - Celtis laevigata Forest

Swietenia mahagoni - Piscidia piscipula - Colubrina arborescens Forest

Taxodium ascendens / Hypericum chapmanii / Rhynchospora harperi Dwarf Woodland

Taxodium ascendens / Magnolia virginiana / Cladium mariscus ssp. jamaicense Forest

Taxodium distichum - Liquidambar styraciflua - Platanus occidentalis / Asimina triloba Forest

Taxodium distichum - Taxodium ascendens / Panicum hemitomon - Sclerolepis uniflora Woodland

Taxodium distichum / Cephalanthus occidentalis / Juncus repens Woodland

Taxodium distichum / Zizania aquatica - Carex canescens ssp. disjuncta Woodland

Thrinax radiata - Casasia clusiifolia - Erithalis fruticosa Forest
Thuja occidentalis - Pinus strobus - Tsuga canadensis / Carex eburnea Woodland

Tsuga canadensis - (Betula alleghaniensis, Quercus rubra) / Ilex montana / Rhododendron catawbiense Forest

Tsuga canadensis - (Liriodendron tulipifera, Fagus grandifolia) / (Magnolia macrophylla, Ilex opaca) / Polystichum acrostichoides Forest

Tsuga caroliniana - (Tsuga canadensis) / Rhododendron maximum Forest

Ulmus americana - Fraxinus pennsylvanica - Celtis laevigata / Glyceria striata - (Carex cherokeensis) Riparian Blackland Woodland

Abies concolor - Chamaecyparis lawsoniana - Picea breweriana / Quercus vacciniifolia Forest

Abies grandis - Picea sitchensis / Gaultheria shallon / Polystichum munitum Forest

Abies grandis / Chrysolepis chrysophylla Forest

Abies grandis / Cornus nuttallii - Acer glabrum Forest

Abies lasiocarpa / Jamesia americana Forest

Abies procera / Oxalis oregana Forest

Acacia koa / Metrosideros polymorpha - Sapindus saponaria Montane Mesic Forest

Acacia koa / Metrosideros polymorpha Montane Mesic Forest

Acacia koa / Santalum paniculatum Montane Mesic Forest

Acacia koa / Sophora chrysophylla Montane Dry Forest

Acacia koaia Lowland Dry Forest

Acer negundo / Betula occidentalis Woodland

Alnus rhombifolia / Betula occidentalis Forest

Alnus rhombifolia / Celtis laevigata var. reticulata Forest

Alnus rhombifolia / Philadelphus lewisii Forest

Alnus rhombifolia / Prunus virginiana Forest

Alnus rhombifolia / Rosa woodsii Forest

Alnus rubra / Adiantum pedatum Forest

Alnus rubra / Athyrium filix-femina - Asarum caudatum Forest

Alnus rubra / Physocarpus capitatus - Philadelphus lewisii Forest

Celtis laevigata var. reticulata / Philadelphus lewisii Woodland

Cercocarpus ledifolius / Holodiscus dumosus Woodland

Chamaecyparis lawsoniana - Picea sitchensis / Vaccinium ovatum - Rhododendron macrophyllum Forest

Chamaecyparis lawsoniana - Pseudotsuga menziesii / (Rhododendron macrophyllum) / Xerophyllum tenax Forest

Chamaecyparis lawsoniana - Tsuga heterophylla / Gaultheria shallon - Rhododendron macrophyllum Forest

Chamaecyparis lawsoniana - Tsuga heterophylla / Polystichum munitum Forest

Chamaecyparis lawsoniana / Rhododendron occidentale Forest

Chamaecyparis lawsoniana / Vaccinium ovatum Forest

Chamaesyce celastroides Montane Dry Woodland

Chamaesyce olowaluana Montane Dry Woodland

Diospyros sandwicensis - Colubrina oppositifolia Lowland Dry Forest

Fraxinus latifolia / Carex deweyana - Urtica dioica Forest

Nestegis sandwicensis / Diospyros sandwicensis Lowland Dry Forest

Nestegis sandwicensis Montane Mesic Woodland

Picea sitchensis - Tsuga heterophylla / Rhododendron macrophyllum - Vaccinium ovatum Forest

Picea sitchensis / Oplopanax horridus / Circaea alpina Forest

Pinus contorta var. contorta / Arctostaphylos columbiana Woodland

Pinus contorta var. contorta / Arctostaphylos uva-ursi Woodland

Pinus contorta var. contorta / Gaultheria shallon - Rhododendron macrophyllum - Vaccinium ovatum Forest

Pinus contorta var. contorta / Gaultheria shallon Forest

Pinus discolor / Quercus gambelii Woodland

Pinus discolor / Quercus rugosa Woodland

Pinus engelmannii / Quercus gambelii Woodland

Pinus flexilis / Purshia tridentata Woodland

Pinus lambertiana - Pinus ponderosa - Pseudotsuga menziesii / Festuca californica Forest

Pinus monticola / Ledum groenlandicum / Sphagnum spp. Woodland

Pinus ponderosa - Quercus garryana / Arctostaphylos viscida / Festuca californica Woodland
Pinus ponderosa / Arctostaphylos patula - Ceanothus velutinus Woodland

Pinus ponderosa / Artemisia tridentata ssp. wyomingensis / Hesperostipa comata Woodland

Pinus ponderosa / Aspidotis densa Woodland

Pinus ponderosa / Carex inops - Festuca roemeri Woodland

Pinus ponderosa / Hesperostipa comata Woodland

Pinus ponderosa / Purshia tridentata / Achnatherum hymenoides Woodland

Pinus ponderosa / Spiraea betulifolia Forest

Pinus radiata Forest

Pinus washoensis Woodland

Pleomele auwahiensis Lowland Mesic Woodland

Populus angustifolia / Salix ligulifolia - Shepherdia argentea Woodland

Populus balsamifera ssp. trichocarpa - Alnus rubra / Carex obnupta Woodland

Populus balsamifera ssp. trichocarpa / Cicuta douglasii Forest

Populus balsamifera ssp. trichocarpa / Cornus sericea / Impatiens capensis Forest

Populus balsamifera ssp. trichocarpa / Crataegus douglasii Forest

Populus balsamifera ssp. trichocarpa / Salix exigua Forest

Populus tremuloides / Acer glabrum Forest

Populus tremuloides / Alnus incana / Betula nana - Ribes spp. Forest

Pouteria sandwicensis - Bobea sandwicensis - Antidesma pulvinatum Forest

Pouteria sandwicensis - Cryptocarya mannii - Diospyros sandwicensis Forest

Pouteria sandwicensis - Pittosporum confertiflorum - Diospyros sandwicensis Forest

Pouteria sandwicensis - Pleomele auwahiensis - Nothocestrum latifolium Woodland

Pritchardia hillebrandii Coastal Mesic Forest

Pritchardia kaalae Lowland Mesic Forest

Pritchardia remota Coastal Dry Forest

Pseudotsuga menziesii - Abies grandis / Symphoricarpos albus / Melica subulata Forest

Pseudotsuga menziesii - Arbutus menziesii / Vicia americana Forest

Pseudotsuga menziesii / Aspidotis densa Woodland

Pseudotsuga menziesii / Symphoricarpos albus - Holodiscus discolor Forest

Quercus emoryi / Sporobolus flexuosus Woodland

Quercus garryana / Carex geyeri Woodland

Quercus garryana / Elymus glaucus Woodland

Quercus garryana / Festuca idahoensis Woodland

Quercus garryana / Pseudoroegneria spicata Woodland

Quercus garryana / Viburnum ellipticum - Toxicodendron diversilobum Woodland

Salix laevigata - Fraxinus velutina Woodland

Sapindus oahuensis Lowland Dry Forest

Sophora chrysophylla / Myoporum sandwicense Subalpine Dry Forest

Thuja plicata - Abies grandis / Polystichum munitum Forest

Thuja plicata / Gaultheria shallon Forest

Tsuga heterophylla - (Thuja plicata) / Sphagnum spp. Forest

Tsuga heterophylla / Ledum glandulosum / Carex obnupta - Lysichiton americanus Forest

Tsuga heterophylla / Rhododendron albiflorum Forest

Picea sitchensis - Tsuga heterophylla / Eurhynchium oreganum Forest

Picea sitchensis / Gaultheria shallon / Maianthemum dilatatum Forest

Picea sitchensis / Malus fusca / Carex obnupta Forest

Pseudotsuga menziesii - (Abies grandis, Thuja plicata) / Mahonia nervosa - Gaultheria shallon Forest

Pseudotsuga menziesii - Tsuga heterophylla - Thuja plicata / Chimaphila umbellata / Rhytidiopsis robusta Forest

Pseudotsuga menziesii / Acer glabrum var. douglasii / Hylocomium splendens Woodland

Pseudotsuga menziesii / Racomitrium canescens Woodland

Thuja plicata - Pseudotsuga menziesii - Tsuga heterophylla / Polystichum munitum - Dryopteris expansa Forest

Tsuga heterophylla - (Abies amabilis) - Picea sitchensis / Oplopanax horridus Forest
Tsuga heterophylla - (Thuja plicata, Pseudotsuga menziesii) / Polystichum munitum - Blechnum spicant Forest

Tsuga heterophylla - Abies amabilis - (Pseudotsuga menziesii) / Hylocomium splendens Forest

Tsuga heterophylla - Abies amabilis / Tiarella trifoliata var. unifoliata - Achlys triphylla - Rubus pedatus Forest

Tsuga heterophylla - Picea sitchensis - (Thuja plicata) / Polystichum munitum - Tiarella trifoliata Forest

Tsuga heterophylla - Picea sitchensis - Abies amabilis / Rubus spectabilis / Polystichum munitum Forest

Tsuga heterophylla - Pseudotsuga menziesii - Thuja plicata - (Abies amabilis) / Achlys triphylla - Gymnocarpium dryopteris Forest

Tsuga heterophylla - Thuja plicata - (Abies amabilis) / Cornus canadensis Forest

Tsuga heterophylla / Hylocomium splendens - Pleurozium schreberi Forest

Abies balsamea - Picea rubens / Danthonia compressa - Lycopodium spp. / Sphagnum spp. Forest

Abies balsamea - Picea rubens / Ilex verticillata / Sphagnum spp. Forest

Acer rubrum - Fraxinus pennsylvanica / Packera aurea - Carex bromoides - Pilea fontana - Bidens laevis Forest

Acer rubrum - Fraxinus pennsylvanica / Polygonum spp. Forest

Chamaecyparis thyoides / Gaylussacia dumosa / Andropogon glomeratus var. glomeratus Woodland

Chamaecyparis thyoides / Rhododendron maximum Forest

Juniperus virginiana - Fraxinus americana / Danthonia spicata - Poa compressa Woodland

Juniperus virginiana - Ostrya virginiana / Carex eburnea Woodland

Juniperus virginiana var. virginiana / Morella pensylvanica Woodland

Picea rubens - (Tsuga canadensis) / Rhododendron maximum Saturated Forest

Picea rubens / Carex trisperma / Sphagnum spp. - Polytrichum spp. Forest

Picea rubens / Rhododendron maximum - Kalmia latifolia / Eriophorum virginicum / Sphagnum spp. Forest

Picea rubens / Vaccinium erythrocarpum / Sphagnum spp. - Bazzania trilobata Forest

Pinus rigida - (Pinus echinata) / Quercus (marilandica, ilicifolia) / Vaccinium pallidum Woodland

Pinus rigida - Quercus coccinea - Quercus falcata / (Quercus marilandica) / Gaylussacia frondosa Woodland

Pinus rigida / Corema conradii Woodland

Pinus rigida / Hudsonia tomentosa Woodland

Pinus rigida / Quercus (marilandica, ilicifolia) / Pyxidanthera barbulata Woodland

Pinus rigida / Quercus ilicifolia - Kalmia angustifolia / Pyxidanthera barbulata Woodland

Pinus rigida / Quercus ilicifolia / Lespedeza capitata Woodland

Pinus rigida / Quercus ilicifolia / Piptatherum pungens Woodland

Pinus strobus - Betula populifolia / Comptonia peregrina / Schizachyrium scoparium Woodland

Pinus taeda - (Quercus falcata, Prunus serotina) / Morella cerifera / Vitis rotundifolia Forest

Platanus occidentalis - Acer saccharinum - Betula nigra - Fraxinus pennsylvanica / Boehmeria cylindrica - Carex emoryi Woodland

Platanus occidentalis - Fraxinus pennsylvanica - Ulmus americana / Cornus sericea Forest

Prunus serotina - Sassafras albidum - Amelanchier canadensis - Quercus velutina / Smilax rotundifolia Forest

Quercus muehlenbergii / Packera plattensis - Parthenium auriculatum - Schizachyrium scoparium Woodland

Tsuga canadensis - Fagus grandifolia - Quercus (prinus, alba) Forest

Betula papyrifera / Corylus cornuta Forest

Betula papyrifera / Corylus cornuta Woodland

Fagus grandifolia - Acer saccharum - Quercus bicolor - Acer rubrum Flatwoods Forest

Fagus grandifolia - Acer saccharum Glaciated Midwest Forest

Fagus grandifolia - Quercus spp. - Acer rubrum - Juglans nigra Forest

Fraxinus pennsylvanica - Ulmus americana / Prunus virginiana Woodland

Larix laricina - Acer rubrum / (Rhamnus alnifolia, Vaccinium corymbosum) Forest

Picea glauca / Linnaea borealis Forest

Picea glauca Alluvial Black Hills Forest

Pinus banksiana - Thuja occidentalis - Picea glauca / Juniperus communis Woodland

Pinus echinata / Rock Outcrop Interior Highland Woodland

Pinus strobus - (Pinus resinosa) Driftless Bluff Forest

Pinus strobus - Abies balsamea - Betula alleghaniensis Driftless Forest

Populus deltoides / Panicum virgatum - Schizachyrium scoparium Woodland

Populus deltoides / Symphoricarpos occidentalis Woodland

Quercus alba - Quercus stellata - Quercus velutina / Schizachyrium scoparium Woodland
Quercus alba - Quercus velutina - Quercus palustris / Carex pensylvanica Woodland

Quercus macrocarpa / Andropogon gerardii - Hesperostipa spartea Woodland

Quercus macrocarpa / Corylus cornuta Woodland

Quercus macrocarpa / Ostrya virginiana Forest

Quercus muehlenbergii - Quercus macrocarpa / Andropogon gerardii Ravine Woodland

Quercus palustris - (Quercus stellata) - Quercus pagoda / Isoetes spp. Forest

Quercus palustris - Quercus bicolor - Acer rubrum Flatwoods Forest

Quercus palustris - Quercus bicolor - Nyssa sylvatica - Acer rubrum Sand Flatwoods Forest

Quercus stellata - Quercus marilandica - Quercus falcata / Schizachyrium scoparium Sand Woodland

Quercus stellata - Quercus marilandica - Quercus velutina - Carya texana / Schizachyrium scoparium Woodland

Quercus stellata / Cinna arundinacea Flatwoods Forest

Thuja occidentalis - Betula alleghaniensis Forest

Thuja occidentalis / Carex eburnea - Pellaea atropurpurea Woodland

Tsuga canadensis - Acer saccharum / (Hepatica nobilis var. acuta) Driftless Forest

(Pinus palustris) - Quercus stellata - Quercus incana / Tetragonotheca ludoviciana Woodland

(Pinus palustris) - Quercus stellata - Quercus marilandica - Carya texana / Tragia urens Woodland

(Pinus palustris, Pinus serotina) / Ctenium aromaticum - Muhlenbergia expansa - Calamovilfa brevipilis Woodland

Acer (barbatum, saccharum) - Juglans nigra - Fraxinus americana / Hybanthus concolor Forest

Acer grandidentatum - Quercus muehlenbergii - Quercus laceyi / Carex edwardsiana - Chaetopappa effusa Southern Edwards Plateau Forest

Acer grandidentatum - Quercus muehlenbergii Forest

Acer rubrum var. trilobum - Liriodendron tulipifera / Ilex opaca var. opaca / Osmunda cinnamomea Forest

Acer rubrum var. trilobum - Nyssa sylvatica / Rhexia mariana var. interior Forest

Acer rubrum var. trilobum - Nyssa sylvatica / Rhododendron canescens - Viburnum nudum var. nudum / Woodwardia areolata Forest

Acer rubrum var. trilobum / Alnus serrulata / Calamagrostis coarctata Saturated Woodland

Acer rubrum var. trilobum / Morella caroliniensis - Gaylussacia frondosa / Andropogon glomeratus - (Sarracenia flava) Woodland

Annona glabra - Conocarpus erectus / Acrostichum aureum Forest

Arbutus xalapensis - Quercus grisea - Juniperus deppeana - Acer grandidentatum - Quercus muehlenbergii Forest

Betula alleghaniensis - Tilia americana var. heterophylla / Acer spicatum / Ribes cynosbati / Dryopteris marginalis Forest

Betula alleghaniensis / Ribes glandulosum / Polypodium appalachianum Forest

Betula alleghaniensis / Sorbus americana - Acer spicatum / Polypodium appalachianum Forest

Carya (glabra, alba) - Fraxinus americana - (Juniperus virginiana var. virginiana) Woodland

Carya glabra - Fraxinus americana - Quercus prinus / Ostrya virginiana / Philadelphus hirsutus Woodland

Carya glabra - Tilia americana var. caroliniana - Acer barbatum / Trillium maculatum Forest

Catalpa bignonioides - Salix nigra / Brunnichia ovata / Eupatorium serotinum Forest

Chamaecyparis thyoides - (Liriodendron tulipifera) / Lyonia lucida Forest

Chamaecyparis thyoides - Pinus elliottii var. elliottii / Nyssa biflora - Acer rubrum var. trilobum / Serenoa repens Forest

Chamaecyparis thyoides - Sabal palmetto Forest

Chamaecyparis thyoides / Cyrilla racemiflora - Cliftonia monophylla - Ilex coriacea Woodland

Chamaecyparis thyoides / Magnolia virginiana - Cliftonia monophylla / Orontium aquaticum - Sphagnum spp. Forest

Chamaecyparis thyoides / Persea palustris / Lyonia lucida - Ilex coriacea Forest

Conocarpus erectus - Rhizophora mangle - Laguncularia racemosa - Metopium toxiferum / Tillandsia spp. Woodland

Crataegus aestivalis Forest

Crataegus rufula Forest

Fagus grandifolia - Magnolia grandiflora - Quercus alba / Carpinus caroliniana - Ostrya virginiana - Ilex opaca var. opaca Forest

Fagus grandifolia - Magnolia grandiflora - Quercus michauxii - Quercus nigra / Rhododendron canescens Forest

Fagus grandifolia - Magnolia grandiflora / Ilex opaca - (Persea borbonia) / Mitchella repens Forest

Fagus grandifolia - Magnolia grandiflora / Ostrya virginiana / Aesculus parviflora Forest

Fagus grandifolia - Pinus glabra - Magnolia grandiflora / Serenoa repens Forest

Fagus grandifolia - Quercus (alba, rubra) / Acer barbatum / Asimina triloba Forest

Fagus grandifolia - Quercus alba / Acer (barbatum, leucoderme) / Solidago auriculata Forest

Fagus grandifolia - Quercus alba / Kalmia latifolia - (Symplocos tinctoria, Rhododendron catawbiense) / Galax urceolata Forest

Fraxinus americana - Carya glabra / Muhlenbergia sobolifera - Helianthus divaricatus - Solidago ulmifolia Woodland
Fraxinus americana - Carya glabra / Symphoricarpos orbiculatus - Rhus aromatica / Piptochaetium avenaceum Woodland

Fraxinus americana - Juglans nigra - Ulmus rubra / Acer barbatum - Ostrya virginiana / Ptelea trifoliata Forest

Fraxinus caroliniana / Crinum americanum - Bacopa caroliniana Forest

Fraxinus caroliniana Seasonally Flooded Forest

Fraxinus pennsylvanica - (Carya aquatica) / Forestiera acuminata / Phanopyrum gymnocarpon Depression Forest

Fraxinus pennsylvanica - Populus heterophylla - Ulmus americana - (Quercus texana) Forest

Fraxinus pennsylvanica / Leersia lenticularis - Carex lupulina Forest

Fraxinus quadrangulata - Juniperus virginiana var. virginiana / Schizachyrium scoparium - Lithospermum canescens Woodland

Gordonia lasianthus / Woodwardia virginica - Osmunda regalis var. spectabilis Forest

Juniperus ashei / Bouteloua (curtipendula, hirsuta) Woodland

Juniperus ashei / Cotinus obovatus / Carex eburnea - Rudbeckia missouriensis Woodland

Juniperus ashei Ozark Clifftop Woodland

Juniperus virginiana var. silicicola - Zanthoxylum clava-herculis - Quercus virginiana - (Sabal palmetto) / Sageretia minutiflora - (Sideroxylon tenax) Woodland

Juniperus virginiana var. virginiana - (Celtis laevigata, Prunus angustifolia, Sideroxylon lycioides) Woodland

Juniperus virginiana var. virginiana - Fraxinus quadrangulata / Symphyotrichum oblongifolium - Panicum flexile - Sedum pulchellum Woodland

Liquidambar styraciflua - Acer rubrum - (Nyssa biflora) / Woodwardia virginica Forest

Maclura pomifera - Diospyros virginiana / Glyceria striata - (Carex cherokeensis) Woodland

Magnolia virginiana - Nyssa biflora - Magnolia grandiflora / Ilex coriacea - Viburnum nudum var. nudum / Solidago patula var. strictula Forest

Magnolia virginiana / Illicium floridanum Forest

Metopium toxiferum - Eugenia foetida - Coccoloba uvifera - Thrinax morrisii / Erithalis fruticosa Forest

Metopium toxiferum - Eugenia foetida - Krugiodendron ferreum - Swietenia mahagoni / Capparis flexuosa Forest

Nyssa biflora - (Acer rubrum) / Ilex opaca / Leucothoe axillaris / Carex atlantica ssp. capillacea Forest

Nyssa biflora - Acer rubrum var. trilobum - Liriodendron tulipifera / Magnolia virginiana - Asimina triloba / Clethra alnifolia Forest

Nyssa biflora - Crataegus opaca - (Fraxinus caroliniana) / Rhynchospora mixta Woodland

Nyssa biflora - Liquidambar styraciflua - Acer rubrum var. trilobum / Clethra alnifolia Forest

Nyssa biflora - Liquidambar styraciflua / Magnolia virginiana / Hamamelis virginiana - Viburnum nudum Forest

Nyssa biflora - Magnolia virginiana - Sabal palmetto - Juniperus virginiana var. silicicola Forest

Nyssa biflora - Magnolia virginiana / Cyrilla racemiflora Forest

Nyssa biflora / Ilex myrtifolia / Carex glaucescens - Eriocaulon compressum Forest

Nyssa ogeche - (Nyssa biflora) Forest

Nyssa ogeche / Ilex myrtifolia / Carex turgescens - Carex striata Forest

Picea rubens - (Abies fraseri) / Vaccinium erythrocarpum / Oxalis montana - Dryopteris campyloptera / Hylocomium splendens Forest

Picea rubens - (Betula alleghaniensis, Aesculus flava) / Viburnum lantanoides / Oxalis montana - Solidago glomerata Forest

Picea rubens - (Tsuga canadensis) / Rhododendron maximum Forest

Picea rubens / Acer rubrum / Maianthemum canadense - (Lycopodium clavatum, Lycopodium dendroideum) Forest

Pinus cembroides - Quercus gravesii - Juniperus flaccida / Salvia regla / Piptochaetium fimbriatum Forest

Pinus cembroides - Quercus grisea - Juniperus flaccida / Salvia regla / Muhlenbergia emersleyi Woodland

Pinus cembroides - Quercus grisea - Quercus emoryi - Juniperus flaccida / Salvia regla / Bouteloua curtipendula Woodland

Pinus cembroides - Quercus grisea - Quercus emoryi / Mimosa dysocarpa / Bouteloua gracilis Woodland

Pinus cembroides - Quercus grisea / Agave lechuguilla / Bouteloua curtipendula Woodland

Pinus cembroides - Quercus grisea / Muhlenbergia montana - Piptochaetium pringlei Woodland

Pinus clausa / Quercus geminata - Quercus myrtifolia - (Quercus laevis) / Garberia heterophylla Forest

Pinus clausa / Quercus geminata - Quercus myrtifolia - Conradina canescens Woodland

Pinus clausa / Quercus myrtifolia - Quercus geminata Woodland

Pinus echinata - (Quercus stellata, Quercus marilandica) / Schizachyrium scoparium - Salvia urticifolia Woodland

Pinus echinata - Pinus taeda - Quercus (alba, falcata, stellata) Forest

Pinus echinata - Quercus (incana, stellata, margarettiae) / Cnidoscolus texanus Woodland

Pinus echinata - Quercus (marilandica, stellata) / Schizachyrium scoparium - Silphium terebinthinaceum - Oligoneuron album Woodland

Pinus echinata - Quercus alba / Viburnum (dentatum, acerifolium) Forest

Pinus echinata - Quercus marilandica / Kalmia latifolia - Symplocos tinctoria Woodland

Pinus echinata - Quercus prinus - Quercus stellata / Vaccinium pallidum / Pityopsis graminifolia var. latifolia Woodland

Pinus echinata - Quercus stellata - Quercus marilandica / Schizachyrium scoparium Woodland
Pinus echinata / Quercus incana / Selaginella arenicola ssp. riddellii Woodland

Pinus elliottii - Quercus nigra - Chamaecyparis thyoides / Cyrilla racemiflora - Vaccinium spp. Forest

Pinus elliottii var. densa / Quercus minima / Panicum abscissum Woodland

Pinus elliottii var. densa / Sabal palmetto / Serenoa repens Woodland

Pinus elliottii var. densa / Sideroxylon salicifolium - Chrysobalanus icaco - Ilex cassine Woodland

Pinus elliottii var. elliottii - (Pinus palustris) / Ilex vomitoria - Serenoa repens - Morella cerifera Woodland

Pinus elliottii var. elliottii - (Pinus serotina) / Aristida beyrichiana - Rhynchospora oligantha - Sarracenia (flava, minor, psittacina) Woodland

Pinus elliottii var. elliottii - Magnolia virginiana - Taxodium ascendens - Nyssa biflora / Polygala cymosa - Carex glaucescens Forest

Pinus elliottii var. elliottii - Taxodium ascendens / Hypericum brachyphyllum / Sporobolus pinetorum - Dichanthelium scabriusculum Woodland

Pinus elliottii var. elliottii - Taxodium ascendens / Polygala cymosa - Rhynchospora spp. Woodland

Pinus elliottii var. elliottii / Cliftonia monophylla - Cyrilla racemiflora Woodland

Pinus glabra - Quercus virginiana - Carya glabra / Carpinus caroliniana / Serenoa repens Forest

Pinus palustris - (Pinus elliottii var. elliottii) / Quercus (chapmanii, myrtifolia) - Serenoa repens / Aristida beyrichiana - Chapmannia floridana Woodland

Pinus palustris - (Pinus elliottii var. elliottii) / Sporobolus pinetorum - Oclemena reticulata - (Sporobolus curtissii) Woodland

Pinus palustris - (Pinus serotina) / Ilex glabra - Gaylussacia frondosa - (Kalmia carolina) Woodland

Pinus palustris - Pinus (echinata, taeda) - Quercus falcata - Carya texana Woodland

Pinus palustris - Pinus (echinata, taeda) / Schizachyrium tenerum - Vernonia angustifolia Woodland

Pinus palustris - Pinus echinata - (Pinus virginiana) / Quercus marilandica - (Quercus prinus) / Vaccinium pallidum Woodland

Pinus palustris - Pinus serotina / Quercus chapmanii - Quercus myrtifolia - Quercus geminata - Lyonia ferruginea Woodland

Pinus palustris - Pinus serotina / Sporobolus pinetorum - (Aristida stricta) - Eryngium integrifolium Woodland

Pinus palustris - Pinus taeda / Quercus geminata - Quercus hemisphaerica - Osmanthus americanus var. americanus / Aristida stricta Woodland

Pinus palustris - Quercus marilandica West Gulf Woodland

Pinus palustris / Amorpha herbacea var. herbacea / Aristida stricta - Sorghastrum nutans Woodland

Pinus palustris / Aristida stricta - Sorghastrum nutans - Anthaenantia villosa Woodland

Pinus palustris / Eryngium integrifolium - Rhynchospora spp. - (Ctenium aromaticum) Woodland

Pinus palustris / Leiophyllum buxifolium / Aristida stricta Woodland

Pinus palustris / Quercus (incana, margarettiae) / Aristida beyrichiana - Asimina angustifolia Woodland

Pinus palustris / Quercus (laevis, myrtifolia) / Aristida beyrichiana - Chapmannia floridana Woodland

Pinus palustris / Quercus incana - Quercus margarettiae / Vaccinium arboreum / Cnidoscolus texanus - Stylisma pickeringii var. pattersonii Woodland

Pinus palustris / Quercus incana - Quercus marilandica / Aristida beyrichiana - Nolina georgiana Woodland

Pinus palustris / Quercus incana - Quercus stellata / Aristida beyrichiana - Sporobolus junceus - Nolina georgiana Woodland

Pinus palustris / Quercus incana / Aristida stricta - Sorghastrum nutans - Anthaenantia villosa Woodland

Pinus palustris / Quercus incana / Schizachyrium scoparium - Croton argyranthemus Woodland

Pinus palustris / Quercus laevis - (Quercus incana) / Vaccinium tenellum / Schizachyrium scoparium - Eriogonum tomentosum Woodland

Pinus palustris / Quercus laevis - Quercus geminata / Vaccinium tenellum / Aristida stricta Woodland

Pinus palustris / Quercus laevis - Quercus incana / Aristida beyrichiana - Baptisia perfoliata Woodland

Pinus palustris / Quercus laevis / Aristida purpurascens - Stipulicida setacea - (Rhynchospora megalocarpa, Selaginella acanthonota) Woodland

Pinus palustris / Quercus laevis / Aristida stricta / Cladonia spp. Woodland

Pinus palustris / Quercus laevis / Gaylussacia dumosa / Aristida beyrichiana - Helianthus atrorubens Woodland

Pinus palustris / Quercus laevis / Serenoa repens - Clinopodium coccineum Woodland

Pinus palustris / Quercus laevis / Serenoa repens - Vaccinium stamineum / Aristida beyrichiana Woodland

Pinus palustris / Quercus laevis / Serenoa repens / Aristida condensata Woodland

Pinus palustris / Quercus margarettiae - Quercus incana / Schizachyrium scoparium Atlantic Woodland

Pinus palustris / Quercus marilandica - Quercus laevis / Aristida beyrichiana - Nolina georgiana Woodland

Pinus palustris / Quercus marilandica / Gaylussacia dumosa / Aristida stricta Woodland

Pinus palustris / Quercus marilandica / Ilex vomitoria / Schizachyrium scoparium Woodland

Pinus palustris / Quercus marilandica / Panicum virgatum Woodland

Pinus palustris / Quercus marilandica / Schizachyrium scoparium - Schizachyrium tenerum - Rhexia alifanus Woodland

Pinus palustris / Quercus marilandica / Vaccinium crassifolium / Aristida stricta Woodland

Pinus palustris / Quercus pumila - Gaylussacia dumosa / Schizachyrium scoparium Woodland

Pinus palustris / Quercus pumila / Aristida beyrichiana Woodland

Pinus palustris / Rhynchospora elliottii - Lobelia flaccidifolia - Platanthera nivea - (Helenium drummondii) Woodland
Pinus palustris / Schizachyrium scoparium - Coreopsis tripteris - Baptisia bracteata var. leucophaea Woodland

Pinus palustris / Schizachyrium scoparium - Liatris pycnostachya Woodland

Pinus palustris / Schizachyrium scoparium - Muhlenbergia expansa - Helianthus radula Woodland

Pinus palustris / Schizachyrium scoparium - Rudbeckia grandiflora var. alismifolia Woodland

Pinus palustris / Schizachyrium scoparium - Schizachyrium tenerum - Silphium gracile Woodland

Pinus palustris / Serenoa repens - Ilex glabra Woodland

Pinus palustris / Serenoa repens - Vaccinium myrsinites / Aristida beyrichiana - Sporobolus curtissii Woodland

Pinus ponderosa - Pinus strobiformis Forest

Pinus remota - Juniperus ashei - Quercus spp. Woodland

Pinus remota / Juniperus pinchotii - Quercus mohriana Woodland

Pinus rigida - (Pinus pungens) / Rhododendron catawbiense - Kalmia latifolia / Galax urceolata Woodland

Pinus rigida / Schizachyrium scoparium - Sorghastrum nutans - Baptisia tinctoria Woodland

Pinus serotina / Cyrilla racemiflora - Lyonia lucida - Vaccinium fuscatum Woodland

Pinus serotina / Ilex glabra / Aristida beyrichiana Woodland

Pinus serotina / Ilex glabra / Woodwardia virginica Woodland

Pinus serotina / Morella cerifera / Osmunda regalis var. spectabilis Woodland

Pinus serotina / Sporobolus floridanus - Aristida beyrichiana Woodland

Pinus strobus / Kalmia latifolia - (Vaccinium stamineum, Gaylussacia ursina) Forest

Pinus taeda - (Pinus echinata) - Quercus alba - Carya alba / Acer barbatum - (Acer leucoderme) Forest

Pinus taeda - Chamaecyparis thyoides - Acer rubrum - Nyssa biflora / Lyonia lucida - Clethra alnifolia Forest

Pinus taeda - Nyssa biflora - Taxodium distichum / Morella cerifera / Osmunda regalis var. spectabilis Forest

Pinus taeda - Quercus hemisphaerica / Osmanthus americanus / Ilex glabra Woodland

Pinus taeda - Quercus laurifolia - Chamaecyparis thyoides - (Quercus virginiana) / Vaccinium elliottii Forest

Pinus virginiana / Vaccinium pallidum / Schizachyrium scoparium - Carex pensylvanica Woodland

Platanus occidentalis - Liriodendron tulipifera - Betula (alleghaniensis, lenta) / Alnus serrulata - Leucothoe fontanesiana Forest

Prosopis glandulosa / Acanthocereus tetragonus Woodland

Prosopis glandulosa var. glandulosa / (Celtis pallida, Phaulothamnus spinescens, Ziziphus obtusifolia var. obtusifolia) Woodland

Quercus (falcata, stellata) / Quercus marilandica / Gaylussacia (baccata, dumosa) Woodland

Quercus (pagoda, phellos, shumardii) - Celtis laevigata / Cornus foemina / Podophyllum peltatum - Hymenocallis occidentalis Flatwoods Forest

Quercus (phellos, pagoda, michauxii) / Ilex opaca var. opaca / Clethra alnifolia / Woodwardia areolata Forest

Quercus alba - Carya glabra - Fraxinus americana / Acer leucoderme / Vitis rotundifolia Forest

Quercus alba - Quercus coccinea - Quercus falcata / Kalmia latifolia - Vaccinium pallidum Forest

Quercus alba - Quercus nigra / Ostrya virginiana / Sabal minor Forest

Quercus alba - Quercus rubra - Quercus prinus - Tilia americana var. caroliniana / Ostrya virginiana Forest

Quercus alba - Quercus stellata - Carya carolinae-septentrionalis / Acer leucoderme - Cercis canadensis Forest

Quercus alba / Acer leucoderme - Ostrya virginiana / Solidago auriculata Forest

Quercus alba / Kalmia latifolia Forest

Quercus arkansana - Quercus incana / Selaginella arenicola ssp. riddellii Woodland

Quercus buckleyi - Fraxinus texensis - Quercus muehlenbergii Forest

Quercus falcata - Tilia americana var. caroliniana - Magnolia grandiflora / Ilex vomitoria Forest

Quercus falcata Flatwoods Forest

Quercus fusiformis - (Quercus stellata) / Schizachyrium scoparium Granite Woodland

Quercus fusiformis - Persea borbonia Forest

Quercus geminata - (Quercus virginiana) / Serenoa repens - Lyonia fruticosa Forest

Quercus geminata / Sabal etonia Forest

Quercus geminata / Serenoa repens - Ilex vomitoria - (Sideroxylon lanuginosum) Forest

Quercus hemisphaerica - Carya glabra - (Quercus virginiana) Forest

Quercus hemisphaerica - Carya glabra - Magnolia grandiflora / Sabal etonia Forest

Quercus hemisphaerica - Carya glabra / Oxydendrum arboreum / Sebastiania fruticosa / Carex baltzellii Forest

Quercus hemisphaerica - Pinus taeda - (Quercus nigra) / Osmanthus americanus var. americanus / Ilex glabra Forest

Quercus hemisphaerica - Quercus geminata / Persea borbonia - Osmanthus americanus Forest

Quercus laceyi - Juniperus ashei Woodland
Quercus laurifolia - Magnolia virginiana - Nyssa biflora / Chasmanthium ornithorhynchum Forest

Quercus laurifolia - Nyssa biflora / Clethra alnifolia - Leucothoe axillaris Forest

Quercus lyrata - Quercus (palustris, phellos) - Liquidambar styraciflua - (Populus heterophylla) Forest

Quercus lyrata - Quercus palustris / Acer rubrum var. drummondii / Itea virginica - Cornus foemina - (Lindera melissifolia) Forest

Quercus lyrata - Quercus phellos - Ulmus americana / Rhynchospora spp. Forest

Quercus lyrata Pond Forest

Quercus marilandica / Schizachyrium scoparium - (Helianthus mollis, Silphium asteriscus, Liatris aspera) Woodland

Quercus michauxii - Quercus (nigra, pagoda) - Liquidambar styraciflua - Pinus taeda Forest

Quercus michauxii - Quercus pagoda / Clethra alnifolia - Leucothoe axillaris Forest

Quercus michauxii / Carpinus caroliniana - Ilex opaca / Leucothoe racemosa Forest

Quercus muehlenbergii - (Juniperus virginiana var. virginiana) Unglaciated Bluff Woodland

Quercus muehlenbergii - (Quercus sinuata) - Carya spp. / Sabal minor / Carex cherokeensis - Chasmanthium sessiliflorum Forest

Quercus muehlenbergii - Juglans major - (Ulmus rubra) / Verbesina virginica Forest

Quercus nigra - Quercus geminata / Lyonia ferruginea - Serenoa repens Forest

Quercus pagoda - Carya cordiformis / Chasmanthium sessiliflorum - Verbesina virginica Forest

Quercus pagoda - Quercus (michauxii, shumardii) - Magnolia grandiflora - (Tilia americana var. caroliniana) / Sabal minor Forest

Quercus pagoda - Quercus michauxii - Quercus alba / Arundinaria gigantea ssp. tecta - Sabal minor / Chasmanthium laxum Forest

Quercus pagoda - Quercus phellos - Quercus lyrata - Quercus michauxii / Chasmanthium latifolium Forest

Quercus palustris - Quercus bicolor / Viburnum prunifolium / Leersia virginica - Impatiens capensis Forest

Quercus palustris Pond Forest

Quercus phellos - Quercus alba / Vaccinium fuscatum - (Viburnum nudum) / Carex (barrattii, intumescens) Forest

Quercus phellos - Quercus nigra / Sabal minor - Sebastiania fruticosa Forest

Quercus phellos / Carex (albolutescens, intumescens, joorii) / Climacium americanum Forest

Quercus prinus - Quercus stellata - Carya glabra / Vaccinium arboreum - Viburnum rufidulum Forest

Quercus prinus / Cornus florida - Amelanchier arborea / Pityopsis graminifolia var. latifolia Woodland

Quercus rubra / Carex pensylvanica - Ageratina altissima var. roanensis Forest

Quercus rubra / Rhododendron catawbiense - Rhododendron arborescens Woodland

Quercus shumardii - Quercus muehlenbergii - Acer (barbatum, leucoderme, saccharum) / Ostrya virginiana Forest

Quercus stellata - (Quercus coccinea) / Quercus marilandica / Vaccinium pallidum - (Vaccinium stamineum) Woodland

Quercus stellata - (Quercus marilandica) / Gaylussacia frondosa Acidic Hardpan Woodland

Quercus stellata - Carya (carolinae-septentrionalis, glabra) - (Quercus marilandica) / Ulmus alata / (Schizachyrium scoparium, Piptochaetium avenaceum) W

Quercus stellata - Carya carolinae-septentrionalis / Acer leucoderme / Piptochaetium avenaceum - Danthonia spicata Woodland

Quercus stellata - Pinus taeda Flatwoods Depression Forest

Quercus stellata - Quercus marilandica var. ashei Interior Highlands Scrub Woodland

Quercus stellata - Quercus muehlenbergii / Schizachyrium scoparium - Sorghastrum nutans Black Belt Woodland

Quercus stellata - Ulmus alata - (Juniperus virginiana var. virginiana) / Sporobolus clandestinus - Monarda fistulosa var. stipitatoglandulosa Woodland

Quercus stellata / Viburnum rufidulum - Forestiera ligustrina / Andropogon gerardii Woodland

Quercus stellata / Viburnum rufidulum / Schizachyrium scoparium - (Sorghastrum nutans, Helianthus eggertii) Woodland

Quercus virginiana - (Celtis laevigata) / Prunus caroliniana Forest

Quercus virginiana - (Juniperus virginiana) - Zanthoxylum clava-herculis / Sideroxylon lanuginosum Woodland

Quercus virginiana - (Pinus elliottii var. elliottii, Sabal palmetto) / Persea borbonia - Callicarpa americana Forest

Quercus virginiana - Carya illinoinensis Woodland

Quercus virginiana - Celtis laevigata / Sabal minor Forest

Quercus virginiana - Pinus clausa / Carya (glabra, pallida) / Serenoa repens Forest

Quercus virginiana - Quercus hemisphaerica - Pinus taeda - Quercus falcata / Persea palustris Forest

Quercus virginiana - Quercus hemisphaerica - Pinus taeda / Persea palustris - Ilex vomitoria Forest

Quercus virginiana - Quercus nigra - Liquidambar styraciflua / Ilex opaca var. opaca / Viburnum dentatum Forest

Quercus virginiana - Quercus nigra / Chasmanthium latifolium Forest

Quercus virginiana - Quercus pagoda - Magnolia grandiflora / Cornus florida / Sanicula sp. Forest

Quercus virginiana / Ilex vomitoria - Sabal minor / Carex cherokeensis - Malvaviscus arboreus var. drummondii Forest

Quercus virginiana / Vaccinium arboreum - Ilex vomitoria Forest

Rhizophora mangle - (Avicennia germinans, Laguncularia racemosa) / Acrostichum spp. Forest
Rhizophora mangle - Laguncularia racemosa - Avicennia germinans - Conocarpus erectus / Jacquinia keyensis Forest

Sabal mexicana - Ebenopsis ebano Forest

Sabal palmetto - (Juniperus virginiana var. silicicola) Woodland

Sabal palmetto - Quercus laurifolia - Quercus virginiana - Magnolia virginiana - Ulmus americana Forest

Sabal palmetto - Quercus virginiana - Ulmus americana - Ficus aurea / Acrostichum danaeifolium - Nephrolepis exaltata Forest

Salix caroliniana / Bacopa caroliniana - Blechnum serrulatum Forest

Salix caroliniana / Decodon verticillatus / Typha latifolia Forest

Salix caroliniana / Sacciolepis striata - Boehmeria cylindrica Woodland

Salix exigua / Baccharis salicifolia - Baccharis neglecta / Schoenoplectus spp. Woodland

Salix gooddingii - Fraxinus velutina Temporarily Flooded Woodland

Taxodium ascendens - Cliftonia monophylla - Pinus elliottii var. elliottii - Chamaecyparis thyoides / Hypericum nitidum - Cladium mariscus ssp. jamaicense Fo

Taxodium ascendens / Annona glabra - Cephalanthus occidentalis - Morella cerifera - Salix caroliniana Forest

Taxodium ascendens / Annona glabra / Bacopa caroliniana Forest

Taxodium ascendens / Aristida palustris Depression Woodland

Taxodium ascendens / Chrysobalanus icaco - Ficus aurea - Persea palustris Forest

Taxodium ascendens / Cyrilla racemiflora - Zenobia pulverulenta Woodland

Taxodium ascendens / Panicum hemitomon - Polygala cymosa Woodland

Taxodium ascendens / Paspalum monostachyum - Rhynchospora microcarpa - Cladium mariscus ssp. jamaicense Woodland

Taxodium ascendens / Rhynchospora microcarpa - Schizachyrium rhizomatum - Muhlenbergia filipes Woodland

Taxodium ascendens / Woodwardia virginica Woodland

Taxodium distichum - Nyssa aquatica - Persea palustris Forest

Taxodium distichum - Nyssa biflora - Acer rubrum - Magnolia virginiana Saturated Forest

Taxodium distichum - Nyssa biflora - Magnolia virginiana - Fraxinus profunda Forest

Taxodium distichum - Nyssa biflora / Berchemia scandens - Toxicodendron radicans / Woodwardia areolata Forest

Taxodium distichum - Platanus occidentalis Edwards Plateau Forest

Taxodium distichum - Platanus occidentalis Ouachita Foothills Forest

Taxodium distichum / Carex hyalinolepis Woodland

Taxodium distichum / Persea palustris - Fraxinus caroliniana - Chrysobalanus icaco / Blechnum serrulatum Forest

Taxodium distichum / Typha angustifolia Woodland

Tilia americana (var. caroliniana, var. heterophylla) - Acer barbatum - Fraxinus americana / Arundinaria gigantea / Tillandsia usneoides Forest

Tilia americana var. heterophylla - Fraxinus americana - (Ulmus rubra) / Sanguinaria canadensis - (Aquilegia canadensis, Asplenium rhizophyllum) Forest

Tsuga canadensis - Acer rubrum - (Liriodendron tulipifera, Nyssa sylvatica) / Rhododendron maximum / Sphagnum spp. Forest

Tsuga canadensis - Betula alleghaniensis / Veratrum viride - Carex scabrata - Oclemena acuminata Forest

Tsuga canadensis - Halesia tetraptera - (Fagus grandifolia, Magnolia fraseri) / Rhododendron maximum / Dryopteris intermedia Forest

Tsuga caroliniana - Pinus (rigida, pungens, virginiana) Forest

Tsuga caroliniana / Kalmia latifolia - Rhododendron catawbiense Forest

Ulmus crassifolia - Carya illinoinensis - Celtis laevigata / Chasmanthium sessiliflorum - Carex cherokeensis Forest

Abies amabilis - Abies concolor / Mahonia nervosa Forest

Abies concolor - Chamaecyparis lawsoniana - Pseudotsuga menziesii / (Mahonia nervosa) / Achlys triphylla Forest

Abies concolor - Chamaecyparis lawsoniana / Quercus sadleriana / Leucothoe davisiae - Rhododendron macrophyllum Forest

Abies concolor - Picea breweriana / Chimaphila umbellata Forest

Abies concolor - Picea breweriana / Gaultheria ovatifolia / Orthilia secunda Forest

Abies concolor - Picea breweriana / Vaccinium membranaceum / Goodyera oblongifolia Forest

Abies concolor - Picea pungens - Populus angustifolia / Acer glabrum Forest

Abies concolor - Pinus monticola / Ribes viscosissimum Forest

Abies concolor - Pinus ponderosa / Amelanchier alnifolia Forest

Abies concolor - Pseudotsuga menziesii / Carex rossii Forest

Abies concolor / Carex siccata Forest

Abies concolor / Juglans major Forest

Abies grandis - Picea engelmannii / Maianthemum stellatum Forest

Abies grandis - Thuja plicata / Achlys triphylla Forest

Abies grandis - Tsuga heterophylla / Clintonia uniflora Forest
Abies grandis - Tsuga heterophylla / Polystichum munitum Forest

Abies grandis / Arctostaphylos nevadensis Woodland

Abies grandis / Coptis occidentalis Forest

Abies grandis / Holodiscus discolor Forest

Abies grandis / Spiraea betulifolia Forest

Abies grandis / Taxus brevifolia Forest

Abies grandis / Vaccinium caespitosum Forest

Abies grandis / Vaccinium membranaceum - Achlys triphylla Forest

Abies lasiocarpa - (Pinus contorta) / Lupinus arcticus ssp. subalpinus Woodland

Abies lasiocarpa / Carex siccata Forest

Acer macrophyllum - Alnus rubra / Polystichum munitum - Tellima grandiflora Forest

Acer negundo - Populus angustifolia / Cornus sericea Forest

Acer negundo / Equisetum arvense Forest

Alnus rhombifolia - Abies grandis Forest

Alnus rhombifolia / Sambucus caerulea Forest

Celtis laevigata var. reticulata / Pseudoroegneria spicata Woodland

Cercocarpus ledifolius / Calamagrostis rubescens Woodland

Cercocarpus ledifolius / Symphoricarpos oreophilus Woodland

Chamaecyparis lawsoniana - Pseudotsuga menziesii / Lithocarpus densiflorus / Gaultheria shallon Forest

Chamaecyparis lawsoniana / Rhododendron occidentale / Carex spp. Temporarily Flooded Forest

Cupressus arizonica / Quercus hypoleucoides Forest

Cupressus arizonica / Quercus turbinella Forest

Cupressus macnabiana Forest

Cupressus sargentii Woodland

Fraxinus latifolia - Populus balsamifera ssp. trichocarpa / Rubus spectabilis Forest

Fraxinus latifolia / Juncus patens Forest

Juglans major / Forestiera pubescens var. pubescens Forest

Juniperus occidentalis / Achnatherum thurberianum Woodland

Juniperus occidentalis / Cercocarpus ledifolius - Symphoricarpos oreophilus Woodland

Juniperus osteosperma / Cercocarpus montanus Woodland

Juniperus osteosperma / Pleuraphis mutica Woodland

Juniperus scopulorum / Artemisia nova Woodland

Juniperus scopulorum / Cercocarpus montanus Woodland

Juniperus scopulorum / Purshia tridentata Woodland

Juniperus scopulorum / Schizachyrium scoparium Woodland

Larix lyallii / Vaccinium membranaceum / Luzula glabrata var. hitchcockii Woodland

Larix lyallii / Vaccinium scoparium / Luzula glabrata var. hitchcockii Woodland

Nestegis sandwicensis Lowland Mesic Forest

Picea (engelmannii X glauca, engelmannii) / Carex disperma Forest

Picea (engelmannii X glauca, engelmannii) / Lysichiton americanus Forest

Picea engelmannii / Acer glabrum Forest

Picea engelmannii / Carex disperma Forest

Picea engelmannii / Packera cardamine Forest

Picea engelmannii / Trifolium dasyphyllum Forest

Picea pungens / Betula occidentalis Woodland

Picea pungens / Dasiphora fruticosa ssp. floribunda Woodland

Picea pungens / Lonicera involucrata Forest

Picea sitchensis / Carex obnupta - Lysichiton americanus Forest

Picea sitchensis / Cornus sericea / Lysichiton americanus Forest

Picea sitchensis / Sphagnum spp. Woodland

Pinus albicaulis - (Abies lasiocarpa) / Carex geyeri Woodland

Pinus albicaulis - Pinus contorta var. latifolia / Penstemon laetus Forest
Pinus albicaulis / Calamagrostis rubescens Woodland

Pinus aristata / Trifolium dasyphyllum Woodland

Pinus attenuata / Arctostaphylos nevadensis Woodland

Pinus contorta var. contorta - Pseudotsuga menziesii / Cladina spp. Forest

Pinus contorta var. contorta / Carex obnupta Forest

Pinus discolor / Piptochaetium fimbriatum Woodland

Pinus discolor / Quercus hypoleucoides Woodland

Pinus discolor / Quercus toumeyi Woodland

Pinus edulis - (Juniperus monosperma, Juniperus osteosperma) / Hesperostipa comata Woodland

Pinus edulis / Andropogon hallii Woodland

Pinus edulis / Muhlenbergia dubia Woodland

Pinus leiophylla / Piptochaetium fimbriatum Woodland

Pinus monticola - Pseudotsuga menziesii / Quercus vacciniifolia - Lithocarpus densiflorus Woodland

Pinus muricata - Arbutus menziesii / Vaccinium ovatum Forest

Pinus ponderosa - Populus tremuloides / Carex spp. - (Poa spp.) Forest

Pinus ponderosa - Pseudotsuga menziesii / Arctostaphylos nevadensis Woodland

Pinus ponderosa - Pseudotsuga menziesii / Penstemon fruticosus Woodland

Pinus ponderosa - Quercus garryana / Balsamorhiza sagittata Woodland

Pinus ponderosa - Quercus garryana / Carex geyeri Woodland

Pinus ponderosa - Quercus garryana / Symphoricarpos albus Woodland

Pinus ponderosa / (Andropogon gerardii, Schizachyrium scoparium) Woodland

Pinus ponderosa / Alnus incana Woodland

Pinus ponderosa / Amelanchier alnifolia Woodland

Pinus ponderosa / Arctostaphylos patula - Arctostaphylos viscida Forest

Pinus ponderosa / Artemisia arbuscula Woodland

Pinus ponderosa / Artemisia tridentata ssp. vaseyana / Poa nervosa Woodland

Pinus ponderosa / Calamagrostis rubescens Forest

Pinus ponderosa / Elymus glaucus Forest

Pinus ponderosa / Juglans major Woodland

Pinus ponderosa / Physocarpus malvaceus Forest

Pinus ponderosa / Purshia tridentata / Achnatherum occidentale Woodland

Pinus ponderosa / Purshia tridentata / Carex inops ssp. inops Forest

Pinus ponderosa / Purshia tridentata / Carex rossii Woodland

Pinus ponderosa / Wyethia mollis Woodland

Platanus wrightii - Alnus oblongifolia / Baccharis salicifolia Forest

Platanus wrightii - Juglans major Forest

Platanus wrightii / Bouteloua curtipendula Forest

Populus angustifolia - Juniperus scopulorum Woodland

Populus angustifolia / Acer grandidentatum Forest

Populus angustifolia / Prunus virginiana Woodland

Populus angustifolia / Rosa woodsii Forest

Populus angustifolia / Salix drummondiana - Acer glabrum Woodland

Populus balsamifera (ssp. trichocarpa, ssp. balsamifera) / Symphoricarpos (albus, oreophilus, occidentalis) Forest

Populus balsamifera ssp. trichocarpa - (Populus tremuloides) / Heracleum maximum Forest

Populus balsamifera ssp. trichocarpa - Alnus rubra / Rubus spectabilis Forest

Populus balsamifera ssp. trichocarpa - Fraxinus latifolia Forest

Populus balsamifera ssp. trichocarpa - Picea sitchensis - (Acer macrophyllum) / Oxalis oregana Forest

Populus balsamifera ssp. trichocarpa / Oplopanax horridus - Acer glabrum Forest

Populus deltoides (ssp. wislizeni, ssp. monilifera) - Salix gooddingii Forest

Populus deltoides (ssp. wislizeni, ssp. monilifera) / Artemisia tridentata Woodland

Populus deltoides (ssp. wislizeni, ssp. monilifera) / Distichlis spicata Woodland

Populus deltoides (ssp. wislizeni, ssp. monilifera) / Forestiera pubescens var. pubescens Forest
Populus deltoides (ssp. wislizeni, ssp. monilifera) / Sparse Forest

Populus deltoides / Carex pellita Woodland

Populus deltoides / Cornus sericea Forest

Populus deltoides ssp. monilifera / Bouteloua curtipendula Woodland

Populus deltoides ssp. wislizeni / Anemopsis californica Forest

Populus deltoides ssp. wislizeni / Poliomintha incana Forest

Populus deltoides ssp. wislizeni / Rhus trilobata Woodland

Populus deltoides ssp. wislizeni / Salix irrorata Forest

Populus deltoides ssp. wislizeni / Schizachyrium scoparium Woodland

Populus fremontii - Fraxinus velutina Woodland

Populus fremontii - Platanus wrightii Forest

Populus fremontii - Salix gooddingii / Baccharis salicifolia Forest

Populus fremontii - Salix gooddingii / Salix exigua Forest

Populus fremontii - Salix gooddingii Woodland

Populus fremontii / Acer negundo Forest

Populus fremontii / Baccharis salicifolia Woodland

Populus fremontii / Muhlenbergia rigens Woodland

Populus tremuloides - Abies lasiocarpa / Pedicularis racemosa Forest

Populus tremuloides - Pinus flexilis Forest

Populus tremuloides / Amelanchier alnifolia / Pteridium aquilinum Forest

Populus tremuloides / Carex obnupta Forest

Populus tremuloides / Carex pellita Forest

Populus tremuloides / Ceanothus velutinus Forest

Populus tremuloides / Ranunculus alismifolius Forest

Populus tremuloides / Ribes montigenum Forest

Populus tremuloides / Rubus parviflorus Forest

Populus tremuloides / Sambucus racemosa Forest

Pritchardia martii Lowland Wet Forest

Pseudotsuga menziesii - Quercus garryana / Symphoricarpos albus Woodland

Pseudotsuga menziesii - Sequoia sempervirens / Polystichum munitum Forest

Pseudotsuga menziesii - Sequoia sempervirens / Rhododendron macrophyllum / Vaccinium ovatum Forest

Pseudotsuga menziesii - Tsuga heterophylla / Mahonia nervosa Forest

Pseudotsuga menziesii - Tsuga heterophylla / Rhododendron macrophyllum - Vaccinium ovatum - Gaultheria shallon Forest

Pseudotsuga menziesii - Tsuga heterophylla / Rhododendron macrophyllum - Vaccinium ovatum Forest

Pseudotsuga menziesii - Tsuga heterophylla / Vaccinium ovatum Forest

Pseudotsuga menziesii / Amelanchier alnifolia Forest

Pseudotsuga menziesii / Festuca occidentalis Forest

Pseudotsuga menziesii / Gaultheria shallon - Holodiscus discolor Forest

Pseudotsuga menziesii / Juniperus osteosperma Forest

Pseudotsuga menziesii / Paxistima myrsinites Forest

Pseudotsuga menziesii / Piptatherum micranthum Woodland

Pseudotsuga menziesii / Quercus rugosa Forest

Pseudotsuga menziesii / Rosa gymnocarpa - Holodiscus discolor Forest

Pseudotsuga menziesii / Symphoricarpos albus / Hieracium cynoglossoides Forest

Quercus emoryi / Piptochaetium fimbriatum Woodland

Quercus garryana - (Fraxinus latifolia) / Symphoricarpos albus Forest

Quercus garryana - Quercus kelloggii / Toxicodendron diversilobum Woodland

Quercus garryana / Ceanothus cuneatus / Festuca idahoensis Woodland

Quercus garryana / Symphoricarpos albus / Carex inops Woodland

Quercus garryana / Symphoricarpos albus / Polystichum munitum Forest

Quercus garryana / Symphoricarpos albus Woodland

Quercus garryana / Toxicodendron diversilobum / Elymus glaucus Woodland
Quercus lobata Woodland

Quercus tomentella Forest

Salix lucida ssp. lasiandra / Urtica dioica ssp. gracilis Woodland

Sophora chrysophylla Subalpine Dry Woodland

Thuja plicata - Tsuga heterophylla / Oxalis oregana Forest

Thuja plicata - Tsuga heterophylla / Whipplea modesta Forest

Thuja plicata / Adiantum pedatum Forest

Thuja plicata / Aralia nudicaulis Forest

Thuja plicata / Linnaea borealis Forest

Thuja plicata / Taxus brevifolia / Asarum caudatum Forest

Tsuga heterophylla / Menziesia ferruginea Forest

Tsuga heterophylla / Quercus sadleriana Forest

Tsuga heterophylla / Rubus pedatus Forest

Tsuga heterophylla / Xerophyllum tenax Forest

Tsuga mertensiana / Streptopus amplexifolius Forest
Common Name Confidence Summary GRank Rounded GRank

1 This floodplain forest occurs on rich, moist high-bench floodplains of rivers that flood every few years in coasG1G2 G1

1 This linear floodplain community occurs on middle fluvial benches along rivers of coastal British Columbia. TG1G2 G1

1 This small-patch community occurs on Vancouver Island and the Gulf Islands of the Strait of Georgia and alsG1 G1 

1 This small-patch forest community occurs on sites with strongly fluctuating water tables within the Georgia BG1 G1 

1 This small-patch forest community occurs on gentle and middle slopes on all aspects within the Georgia BasG1 G1 

1 This linear forest plant community occurs on rich, moist, high bench floodplains of rivers that flood every few G1G2 G1 

Cape May Lowland Swamp 2 Typically this community occupies the headwaters of streams in coastal southern New Jersey where occurreG1 G1

Potomac River Bedrock Terrace Oak - Hickory Forest 2 This dry oak-hickory forest occurs on elevated bedrock terraces above the Potomac River for several miles bG1G2 G1

Long Island Maritime Beech Forest 1 This maritime forest community is currently described from north-facing exposed bluffs and the back portions G1 G1

Central Appalachian Circumneutral Seepage Swamp 1 This community is a lush, circumneutral, seepage-fed, mixed woodland or forested swamp of the Allegheny MG1 G1 

Maritime Holly Forest 2 This type represents maritime holly forest of the lee sides of backdunes in New Jersey and Long Island, New G1 G1

Central Coastal Plain Basin Swamp 2 This seasonally flooded hardwood forest community occurs in groundwater basins on the Coastal Plain of MG1G2 G1

ium rugosum Woodland 2 This community occurs on west-facing side ridges of Pike Knob, Pendleton County, W G1 G1 est Virginia, at about 1

Red Pine / Minniebush Forest 2 This red pine forest association is known from high elevations in Pendleton and Hardy counties, W G1 G1 est Virgin

Allegheny Pitch Pine - Red Spruce Peat Swamp2 This coniferous swamp of the Allegheny Mountains of West Virginia and the Catskills of New York occurs on G1G2 G1 

Mesic Pine Barrens 2 This mesic pine barren community is restricted to the eastern portion of the High Allegheny ecoregion. Unlike G1 G1

Pitch Pine - Reedgrass Savanna 2 Pitch pine saturated woodland known to date only from the New Jersey Pine Barrens. The community is chaG1 G1

Pitch Pine - Blueberry Peat Swamp 2 This northern pitch pine swamp occurs in poorly drained depressions in sand plains of the Great Lakes plain G1G2 G1

Loblolly Pine Dune Woodland 1 This maritime woodland occurs on large, xeric sand dunes of barrier islands in Delaware, Maryland, and VirgG1G2 G1 

Chesapeake Bay Tall Maritime Shrubland 2 This association comprises tall, temperate, deciduous maritime shrublands or scrub forests of the mid-AtlantG1G2 G1

Piedmont / Central Appalachian River-Scour W2oodland This community type is restricted to the active channel shelves of large rivers, at localities where bedrock ouG1G2 G1 

North Atlantic Coastal Plain Dry Calcareous Forest 2 This dry, open, calcareous forest of the Coastal Plain of Virginia and Maryland is restricted to subxeric to xerG1 G1

White Spruce / Grouseberry Forest 1 This white spruce community type is found in the Black Hills region of the United States. It had been found aG1G2 G1

Cottonwood Dune Woodland 2 This community occurs in dune fields and on the most stable dune ridges in the southern Great Lakes region G1G2 G1

Cottonwood - Sycamore Forest 2 This cottonwood - sycamore floodplain forest is found in the central Great Plains of the United States. Stands G1G2 G1

Central Midwest White Oak - Mixed Oak Woodland 2 This white oak - mixed oak - hickory woodland type is found in the central tallgrass region of the United StateG1Q G1

Bur Oak Bottomland Woodland 2 This bur oak - swamp white oak woodland community is found in the midwestern United States. Stands occuG1 G1

Western Tallgrass Bur Oak Mesic Woodland 2 This bur oak woodland occurs in the central-western tallgrass prairie region of the United States. Stands occG1G2 G1

Bur Oak / Sedge Woodland 2 The <i>Quercus macrocarpa / Carex inops ssp. heliophila</i> type has been provisionally applied to the exteG1G2 G1

Post Oak - White Oak Dry-Mesic Barrens 2 This post oak - white oak dry-mesic barrens community is found in the Interior Low Plateau of the United StaG1 G1

Western Mayhaw Pond 1 This Gulf Coastal Plain community is comprised of <i>Crataegus</i>-dominated depression forests (5-10 m tG1 G1 

Fraser Fir Forest (Evergreen Shrub Type) 1 This community occurs as island-like stands in the southern Appalachian Mountains of eastern Tennessee, aG1 G1

Fraser Fir Forest (Deciduous Shrub Type) 1 This community occurs as island-like stands in the southern Appalachian Mountains. It occurs on steep ridgeG1 G1

Upper East Gulf Calcareous Bluff Forest 2 This association is known from moist, north-facing, calcareous bluffs in the Upper East Gulf Coastal Plain of G1G2 G1

Lampasas Cutplain Bigtooth Maple Canyon Forest 2 This association includes mesic canyon forests of the Lampasas Cutplain, in the northeastern Edwards PlateG1 G1

2 This community occurs in canyons of the Chisos Mountains of Trans-Pecos Texas. It is codominated by <i>AG1 G1

Montane Floodplain Slough Forest 2 This community occurs in floodplain depressions in the Blue Ridge of North Carolina and possibly TennesseG1 G1

Pond Apple Slough 1 This short forest occurs in semipermanently flooded (10- to 12-month hydroperiod) depressions filled with weG1G2 G1

1 This community occurs in the Chisos Mountains of Trans-Pecos Texas. Evergreen canopy species include <G1 G1

Inland Tropical Hardwood Hammock 2 This association represents south Florida inland hardwood hammocks which were apparently first studied by G1G2 G1

Atlantic Coastal Plain Wet Marl Flatwoods Forest 2 This wet marl forest of the North Carolina Coastal Plain has well-developed tree, subcanopy, and herb layersG1 G1

Florida Keys Coastal Berm Tropical Hammock1 These are diverse hammock forests of the Florida Keys, developed not on consolidated rock, but on storm-dG1 G1

2 This association is a calcareous coastal fringe forest of the Mid-Atlantic Coastal Plain of North Carolina and pG1G2 G1 

2 This community occurs along the Rio Grande throughout the floodplain and delta region in southern Texas aG1G2 G1

2 Wetland hammock islands surrounded by wet prairie, dominated by a 4- to 15-m tall canopy of <i>ConocarpuG1? G1

Florida Keys Wetland Thornscrub 2 This forest is 3-7 m tall, with a diverse canopy (usually no species with more than 25% cover) codominated bG1 G1 

1 This association exhibits a scattered to open canopy of <i>Conocarpus erectus</i> over a grassy herb layer. G1? G1

Atlantic Coast Stiff Dogwood Dune Swale 1 This association represents peaty wetlands developed in old interdune swales along the North Carolina coasG1 G1

Texas Ebony Resaca Forest 2 This evergreen subtropical community once occurred as dense forests with 15-m canopies and large-diametG1 G1

East Gulf Coastal Plain Calcareous Bluff Beech - Magnolia Forest 1 This is the most calcareous association of beech - magnolia forest. It occurs over calcareous rock or sedimeG1G2 G1

Southern Loess Hills Hardwood - Pine Forest 1 This association represents the mixed hardwood - pine forests on strongly loess-influenced loam soils in the G1G2 G1
Southern Appalachian Beech Gap (North Slope Tall Herb Type) 1 This association includes stunted beech forests of the southern Appalachians, occurring on north-facing upp

G1 G1

Southern Appalachian Beech Gap (South Slope Sedge Type) 1 This association is often referred to as a classic "beech gap" forest and includes vegetation with short-statureG1 G1 

Southeast Florida Tropical Maritime Hammock2 This type includes tropical maritime hammocks of the southeastern coast of Florida. The very diverse canopy G1 G1

Southwest Florida Tropical Maritime Hammock2 This association represents tropical maritime hammocks of the southwestern coast of Florida. In comparison G1 G1

Tidal Ash - Elm Forest 2 These are tidal forests, dominated by <i>Fraxinus pennsylvanica, Ulmus americana, Acer rubrum var. trilobuG1G2 G1

Bluegrass Cane Woodland 2 This historic community was restricted to the Bluegrass Region of Kentucky. The tree layer was dominated bG1 G1 

Bluegrass Basin Black Walnut Canebrake Forest 2 This community represents deep-soil vegetation of calcium-rich areas in the Bluegrass Basin of Kentucky, thG1 G1

Tidal Red-cedar Woodland 2 Infrequently flooded brackish (oligohaline) woodlands along tidal creeks about 25-35 km by river distance froG1? G1

Sweetgum Coastal Plain Lakeshore Forest 2 This natural lakeshore forest is dominated by <i>Liquidambar styraciflua</i>; the subcanopy is dominated by G1 G1

Texas Upper West Gulf Coastal Plain Southern Magnolia Forest 1 This is a mostly evergreen-dominated hardwood forest found along the periphery of the W G1? G1 est Gulf Coastal P

Everglades Bayhead Forest (Shark Slough Type) 2 This bayhead community occurs in the Shark River Slough portion of the Everglades region of southern FlorG1 G1 

1 Similar to tropical bayheads but with an open canopy and a much better developed herbaceous stratum. The G1 G1

2 This is an open woodland, the open structure perhaps maintained in part by prescribed burning, growing on eG1 G1

Water Tupelo Sinkhole Pond Swamp 2 This water tupelo sinkhole pond type is found in the south-central midwestern United States, from southeasteG1? G1

2 This flatwoods pond community is known from the East Gulf Coastal Plain of Louisiana and possibly MississG1? G1 

2 This vegetation occurs in seasonally flooded upland pools in the lower Piedmont of North Carolina. VegetatioG1 G1

2 This vegetation occurs in seasonally flooded upland ponds in the Ridge and Valley and adjacent Cumberland G1G2 G1 

Maritime Red Bay Shrub Swamp 2 This forest occurs on peaty soils only slightly above sea level, in swales and seepage-fed areas adjacent to sG1 G1 

Red Spruce - Fraser Fir Forest (Evergreen Shrub Type) 1 This community is restricted to the highest mountain systems of the southern Appalachians in eastern TenneG1 G1

Red Spruce - Northern Hardwood Forest (Shrub Type) 2 This association occurs in the broad elevational transition zone between spruce-fir and northern hardwoods G1? G1

Appalachian Red Spruce Boulderfield Forest 1 This association includes steep, seepy boulderfields dominated by <i>Picea rubens</i>, found at slightly highG1 G1

Sand Pine Maritime Hammock 2 This forest occurs in xeric sands in mainland areas near the coast in the Florida Panhandle. The closed canoG1G2 G1 

Peninsular Open Sand Pine / Rosemary Scrub1 This scrub vegetation of the Florida peninsula is characterized by an emergent layer of <i>Pinus clausa</i> aG1 G1

Panhandle Open Sand Pine / Rosemary Scrub1 This scrub community of the Florida panhandle coast has an emergent layer of <i>Pinus clausa</i> above a G1G2 G1

Lake Wales Sand Pine Scrub 1 This Lake Wales Ridge scrub association is limited to Highlands and Polk counties, Florida. It is characterizeG1G2 G1

East Gulf Coastal Plain Shortleaf Pine - Post Oak Forest 2 This <i>Pinus echinata - Quercus stellata</i> community occurs on dry, acid, loamy to clayey uplands in the G1 G1

West Gulf Coastal Plain Shortleaf Pine - Post Oak W 2 This <i>Pinus echinata - Quercus stellata</i> woodland occurs on dry, acid, loamy to clayey uplands in the W oodland G1 G1 

Piedmont Shortleaf Pine - Oak Mafic Slope Barrens 2 This association includes Piedmont woodlands on soils derived from mafic rock (metavolcanics of the CarolinG1? G1

Ouachita Shortleaf Pine Savanna 2 This upland subxeric woodland community was a matrix forest type in the Ouachita Mountains and, historicaG1G2 G1

Florida Keys Pine Rockland 1 This community is characterized by a 7- to 13-m open canopy of <i>Pinus elliottii var. densa</i> over a well-dG1 G1

South Florida Pine Prairie 2 This community has estimated hydroperiods of 1-45 days per year, averaging six days per year, though satuG1G2 G1

Miami Rock Ridge Pine Rockland 1 This community has an open canopy of <i>Pinus elliottii var. densa</i> occurring over a low-shrub layer and G1 G1

Louisiana Wet Spruce Pine - Hardwood Flatwoods Forest 2 This community occurs on hydric, acidic silt loams (Encrow, Gilbert, and Springfield series), on broad, low flaG1G2 G1

Southern Mississippi Claypan Flatwoods 1 This association is a saturated longleaf pine woodland found on sandy soil over an underlying clay layer in thG1? G1

Atlantic Coastal Plain Mesic Longleaf Pine - Little Bluestem W 1 This longleaf pine woodland occurs on upland flats on sandy loam soils of the inner Atlantic Coastal Plain. Toodland G1 G1

West Gulf Coastal Plain Fire-Infrequent Xeric Sandhill 2 This xeric forest develops on fuel-limited, xeric, deep sands within the range of <i>Pinus palustris</i> in the W G1G2 G1 

Atlantic Coastal Plain / Wet Ultisol Longleaf Pine Savanna 2 This seasonally saturated longleaf pine - pond pine - loblolly pine woodland association is restricted to wet aG1 G1

Georgia Piedmont Longleaf Pine Serpentine W1oodland This community is characterized by a 10- to 14-m canopy of <i>Pinus palustris</i> and <i>Pinus echinata</i> G1 G1

1 This community occupies wet flats; this includes flatwoods of the South Atlantic Coastal Plain. Stands are doG1G2 G1

2 This saturated longleaf pine - slash pine woodland community occurs in pineland swales and is restricted in dG1 G1

Longleaf Pine / Pond Pine Savanna (Wet Ultisol Type) 1 This association is a saturated longleaf pine - pond pine woodland which is found on wet Ultisols of the AtlanG1 G1

2 This saturated longleaf pine - pond pine woodland community occurs in the South Atlantic Coastal Plain of SG1 G1

1 This saturated longleaf pine - pond pine woodland community occurs in the Mid-Atlantic Coastal Plain of NorG1 G1

Longleaf Pine Savanna (Wet Pleea Flat Type)1 This saturated longleaf pine - pond pine woodland association is only found on wet flats of the Atlantic CoastG1 G1

Atlantic Coastal Plain Very Wet Clay Longleaf Pine Savanna 1 This saturated longleaf pine - pond pine woodland association is only found on very wet clay soils of the AtlaG1 G1

Lower Piedmont Wet Longleaf Pine Woodland1 This is a wet longleaf pine community of the lower Piedmont of North Carolina (Moore, Montgomery, and AnG1 G1

Longleaf Pine Savanna (Lumbee Type) 1 This saturated longleaf pine - loblolly pine - pond pine woodland occupies wet-mesic savannas on loamy soiG1 G1

ia minor Woodland 2 The open canopy of this association is dominated by <i>Pinus palustris</i>. The woody understory may contG1 G1

2 The open canopy of this association is dominated by <i>Pinus palustris</i>. The woody understory may contG1 G1

1 This association is an upland longleaf pine community occurring on rolling, clay-based hills and upland flats iG1G2 G1

Western Upland Longleaf Pine Forest (Stream Terrace Sandy W 1 This community occurs on fine-sandy stream terraces in the W oodland Type) G1?Q est Gulf Coastal Plain of Louisiana and TexasG1

Eastern Louisiana Xeric Longleaf Woodland 1 This xeric <i>Pinus palustris</i> association occurs in the Florida parishes of eastern Louisiana and may ranG1G2 G1
1 This xeric longleaf pine sandhill community occurs on xeric ridges in north-central peninsular Florida and on 

G1G2 G1

Longleaf Pine / Scrub Oak Sandhill (Northern Type) 1 This association is a longleaf pine / scrub oak sandhill community north of the range of <i>Aristida stricta</i> G1 G1

Sandstone/Gravel Longleaf Pine Woodland 1 The open to scattered canopy consists of <i>Pinus palustris</i>. A sparse scrub oak layer consists of <i>QueG1 G1

West Gulf Coastal Plain Calcareous Clay Longleaf Pine Glade 1 This small-patch <i>Pinus palustris</i> community is associated with outcroppings of calcareous and/or high G1 G1 

Louisiana Longleaf Pine Fleming Glade 1 This sparse woodland is dominated by a scattered, somewhat stunted <i>Pinus palustris</i> canopy; <i>QueG1 G1

Atlantic Coastal Plain / Wet Ultisol Longleaf Pine Savanna 2 This seasonally saturated longleaf pine - pond pine - loblolly pine woodland association is restricted to wet aG1? G1 

Western Wet Longleaf Pine Savanna (Prairie Terraces Sodic Silt Loam Type) 1 This association is a West Gulf Coastal Plain wetland longleaf community, occurring on saline soils (BrimstoG1 G1

1 This is a mesic longleaf pine-dominated association, with few oaks. It occurs on relict terraces along deeply eG1 G1

Southern Blue Ridge Ultramafic Outcrop Barrens (Pitch Pine W 1 This community includes open woodland vegetation dominated by stunted <i>Pinus rigida</i> and <i>Quercuoodland Type) G1 G1

Southern Blue Ridge Ultramafic Woodland (Prairie Type) 1 This association represents upland ultramafic woodlands of the Southern Blue Ridge of Virginia. Examples aG1 G1

1 This woodland occurs in association with large peat domes in the tidewater region of North Carolina and VirgG1 G1 

Low-Elevation Blue Ridge Serpentine Woodland1 This community includes pine-oak woodlands over serpentine, olivine, dunite, and other ultramafic rocks, at eG1 G1

Crowley's Ridge Mesic Oak Forest 2 This mesic oak forest occurs on rich, loessal soils of southern Crowley's Ridge on narrow ridgetops and side G1G2 G1

Piedmont Diabase White Oak Woodland 2 This is a fire-maintained woodland of the Piedmont of Virginia, occurring on soils derived from diabase rock. G1? G1

Southern Crowley's Ridge Dry-mesic Oak Forest 2 This dry-mesic oak forest occurs on rich, loessal soils of the southern portion of Crowley's Ridge, Arkansas, G1G2 G1

Piedmont Granitic White Oak - Black Oak Savanna 2 This is a fire-maintained woodland of the Piedmont of Virginia and South Carolina, occurring on soils derived G1? G1

Ouachita Mountains Dwarf White Oak Forest 1 This community is characterized by a nearly continuous canopy of gnarled <i>Quercus alba</i>, 2.5-5.0 m taG1 G1

Southern Blue Ridge Ultramafic Outcrop Barrens (Deciduous Forest Type) 1 This community includes <i>Quercus alba</i>-dominated forest vegetation occurring in association with serpG1 G1

Bluegrass Basin Swamp White Oak Forest 2 This swamp forest is a high-fertility wetland, which is restricted in its distribution to the Inner and Outer BluegG1G2 G1 

Atlantic Coastal Plain Mixed Deciduous Maritime Forest 2 This community and related deciduous-dominated communities occur on the most sheltered sites on barrier G1 G1

Oak - Sabal Tropical Hydric Hammock 2 This association includes slightly higher hammock islands surrounded by wet prairies of southern Florida. ThG1? G1

Sinking Pond Overcup Oak Swamp 2 This forest is found in an apparently unique isolated upland depression of the Eastern Highland Rim of TennG1 G1

Alabama Ketona Dolomite Woodland 1 This association covers woodlands over Ketona dolomitic limestone, in Bibb County, Alabama, associated wG1 G1

Highland Rim Upland Depression Flatwoods 2 This association included forests in upland karst depressions over Fort Payne Formation cherty limestone in G1? G1

Appalachian Calcareous Oak - Walnut Forest 2 This association represents forests on sheltered dolomite slopes in the Southern Blue Ridge with canopies dG1Q G1

2 This mesic calcareous upland woodland community occurs in areas of deep, moist soil usually on nearly leveG1 G1 

Keiffer Prairie Margin Oak-Ash-Hickory Forest2 This West Gulf Coastal Plain calcareous forest is currently known only from the Keiffer Prairie Research NatG1Q G1

Jackson Formation Calcareous Forest 2 This mesic forest community is restricted to calcareous soils associated with the Jackson Formation in the W G1 G1 

Calcareous Oak - Hickory High Bottomland Forest 2 This West Gulf Coastal Plain forest occurs on calcareous Alligator clay in Caldwell Parish (and possibly also G1 G1

Dry-Mesic Copenhagen Calcareous Forest 2 This upland forest community is known only from dry-mesic slopes associated with Jackson Calcareous PraiG1 G1

Piedmont Basic Hardpan Woodland (Northern Type) 2 This community consists of one of two prairie-like woodlands associated with diabase in the Carolina PiedmoG1 G1

Piedmont Basic Hardpan Woodland (Southern Type) 2 This community consists of one of two prairie-like woodlands associated with diabase in the Carolina PiedmoG1 G1

East Texas Catahoula Barrens Post Oak Woodland 2 This community is found along margins and along broad intermittent drainages associated with Catahoula BaG1 G1 

Southern Crowley's Ridge Dry Post Oak Forest2 This forest appears to be the driest upland community present in the loessal region of southern Crowley's RiG1 G1

Upper West Gulf Coastal Plain Prairie Periphery Oak W 2 This subcalcareous or circumneutral vegetation of the Upper W oodland G1G2 est Gulf Coastal Plain is dominated by <i>QuG1

Gulf Coast Salt Dome Hardwood Forest 2 This association includes upland forests on loess-derived silt loams of coastal salt domes of Louisiana and uG1 G1

Virginia Beach Xeric Dune Forest 2 This maritime woodland occurs primarily on back dunes that are somewhat protected from regular salt spray G1 G1

2 This community occurs on low moist to wet flats, near the conceptual line between upland and saturated hydG1G2Q G1 

2 This forest occurs on mesic to dry-mesic bluffs in the outer Coastal Plain of southeastern South Carolina. ThG1Q G1

Everglades Bayhead Forest (Taylor Slough Type) 2 This bayhead community occurs in the Taylor Slough portion of the Everglades region of southern Florida. It G1 G1 

2 This association represents a wet swamp hammock forest of southern Florida. The sparse supercanopy is doG1 G1 

1 Tropical maritime hammocks of the southwestern coast of Florida, less well-developed and diverse than highG1 G1

2 This community occurs on similar sites to <i>Pinus elliottii var. densa</i> communities but with more frequenG1G2 G1

South Florida Indian Midden Hammock 2 This hardwood hammock community occurs on Indian middens in southern Florida. These forests are closelG1Q G1

South Florida Madeira Hammock 2 This tropical hammock type occurs in the southern coastal portions of Everglades National Park. <i>SwietenG1Q G1

West Florida Coat-Rack Cypress Savanna 2 This dwarf pond-cypress savanna is a highly unusual association, which is dominated by a rather open, esseG1 G1

Gulf Coast Pond-cypress Dune Swale 2 This community is found in interdune swales on barrier islands along the Alabama Gulf coast. <i>Taxodium aG1 G1 

Blackwater Lake Shoreline Forest 2 This association covers deciduous forests on mineral soils on the edge of blackwater lakes in the Tidewater G1? G1

Atlantic Coastal Plain Cypress Lakeshore 2 This natural lake shoreline community of the Outer Coastal Plain of North Carolina has an open (locally closeG1 G1

Lake Drummond Pond Shore 2 This community occurs on the sandy and peaty, seasonally flooded shores of Lake Drummond (Great DismaG1? G1 

Mid-Atlantic Tidal Cypress Woodland 2 This community is known from the Northwest River, Virginia. It occurs on oligotrophic, somewhat quaking peG1Q G1

Fan Palm Hammock 2 Coastal berm vegetation of extreme southern peninsular Florida. <i>Thrinax radiata, Casasia clusiifolia</i>, aG1Q G1
Southern Appalachian Northern White-cedar Slope W 2 This is essentially a mixed coniferous-deciduous woodland of the southern and central Appalachians, with ea

oodland G1G2 G1

Eastern Hemlock / Catawba Rhododendron Forest 2 This community type is known only from seven locations in the northern Blue Ridge and Ridge and Valley reG1? G1

Cumberland Plateau Mesic Hemlock - Hardwood Forest 2 This association represents acidic forests dominated by <i>Tsuga canadensis</i> and mesic hardwood specG1G2 G1

Carolina Hemlock Forest (Mesic Type) 2 This association encompasses <i>Tsuga caroliniana</i> forests on valley bottoms, gorge slopes, or other proG1G2 G1

 Blackland Woodland 2 This riparian mesic blackland woodland community occurs in deep soils on relatively level terrain, typically as G1? G1

1 This association occurs at moderate elevations of 1285-1420 m (4220-4650 feet) on northerly aspects in souG1 G1

1 This is a coastal, coniferous forest known only from the southwestern Oregon coastal zone, and is the only aG1 G1

2 This mixed conifer association occurs on the eastern slope of the Oregon Cascades and is most often found G1 G1

2 This closed to open forest occurs in the east Cascades of Washington near Mount Adams. This association G1 G1

2 This high-elevation forest is dominated by <i>Abies lasiocarpa</i>. <i>Picea engelmannii</i> is not present. G1 G1 

2 This association is known from the northern Oregon Coast Range, and is assumed to be extirpated from the G1 G1 

2 G1 G1

2 G1 G1

2 G1 G1

2 G1 G1

2 G1 G1

2 In Colorado these riparian woodlands grow in narrow, sandstone box canyons of western Colorado. Stands aG1G2 G1

1 This plant association is described from data collected in the Snake and Salmon river corridors, within the BlG1 G1

1 This riparian plant association is described from data collected in the Snake and Salmon river corridors, withG1? G1

1 This riparian plant association is known from data collected in the Snake and Salmon river corridors, within thG1 G1

1 This riparian plant association is reported from data collected in the Snake and Salmon river corridors, within G1? G1

1 This plant association is described from data collected in the Snake and Salmon river corridors, within the BlG1 G1

1 <i>Alnus rubra / Adiantum pedatum</i> is an early-seral community type that occurs on well-drained, moderaG1 G1

2 Found only along two streams on the northwestern slope of the Blue Mountains of Oregon and W G1 G1 ashington a

1 Found only along a few streams on the northwest slope of the Blue Mountains of Oregon and W G1 G1 ashington, th

2 This is a riparian shrubland or short woodland community known only in the vicinity of the common border of G1 G1 

2 This association is described from stands located on the slopes of Germer Peak, Idaho, within the Challis VoG1G2 G1

2 This coastal forest is restricted to marine terraces along the southern Oregon and potentially extreme northeG1 G1

1 This coniferous forest association is found in southwestern Oregon and northwestern California between 720G1 G1

2 This conifer forest association is found on mesic sites between 450-700 m elevation on sedimentary substratG1 G1

1 This giant conifer association grows on mesic sites between 300-800 m elevation in southwestern Oregon anG1 G1

2 This is an open-canopy, coniferous forest found on metamorphic substrates, primarily serpentine and gneissG1 G1

1 This naturally rare, edaphically specialized, coniferous forest is extremely limited in range. Only a few stands G1 G1

2 G1 G1

2 G1 G1

2 G1 G1

2 This mid-seral association occurs on floodplains along the middle reaches of the lower Columbia River in OreG1 G1 

2 G1 G1

2 G1 G1

1 This association occurs along the Pacific coast between northern California and Tillamook Bay, Oregon. StaG1 G1

1 This plant association is found only on hill slopes adjacent to the Stikine River Delta, Alaska. W G1 G1 indblown silt 

1 This woodland association occurs discontinuously along the Pacific coast between northern California and TG1 G1

1 These woodlands are found discontinuously along the coast between northern California and southwestern W G1 G1 

1 This association occurs on flat to depressional topography with impeded drainage, usually on ancient marine G1 G1

1 G1G2 G1

2 This Madrean conifer woodland has been documented only from the Animas Mountains in extreme southwesG1 G1

2 G1 G1

2 G1 G1

2 This woodland association is known from stands located on recent, relatively unweathered mafic lava flows oG1? G1

1 Average elevation for this association is 930 m (3050 feet); aspect is variable, though generally not north. SloG1 G1

2 This association is found in bogs or poor fens in the central and northern Puget Lowlands of W G1 G1 ashington. So

2 This is an open woodland or savanna with widely spaced <i>Pinus ponderosa</i> and <i>Quercus garryana<G1 G1 
1 This is a Ponderosa pine woodland known from interior valleys in southwestern Oregon and northwestern Ca

G1 G1

1 These woodlands are open, sparse woodlands on isolated sand dunes and sandy flats. There are only two kG1 G1

2 This open woodland association has been described from the eastern side of the Cascades Range, a mountG1 G1

2 G1 G1

1 This association includes <i>Pinus ponderosa</i> stands generally on coarse-textured soils with few or no shG1 G1

1 <i>Pinus ponderosa</i> dominates the tree layer of this open woodland. Scattered individuals of <i>JuniperuG1 G1

2 This is a montane woodland or forest type found on mesic sites on the eastern flank of the Bighorn MountainG1G2 G1 

2 This association is a forest dominated by <i>Pinus radiata </i>found on marine terraces and headlands of thG1 G1

2 <i>Pinus washoensis</i> is the sole or dominant tree in the canopy. <i>Pinus contorta var. murrayana, Pinus G1? G1

2 G1 G1

2 This riparian woodland has an extremely limited distribution in western Colorado. Historically, it was more widG1 G1

2 G1 G1

1 This riparian forest of the Columbia Basin grows on stream terraces between 400-750 m of elevation. W G1 G1 inter

2 This mid-seral association occurs on floodplains along the middle reaches of the lower Columbia River in OreG1 G1 

1 This riparian forest association occurs along tributaries to the Grande Ronde River in the foothills zone of the G1 G1 

2 This association occurs on alluvial deposits along rivers and perennial streams in habitats which are seasonaG1 G1

2 This uncommon <i>Populus tremuloides</i> forest association is found in a mountainous region east of the CG1G2 G1

2 This is a valley bottom, riparian forest known only from the Wallowa River valley in northeastern Oregon. The G1 G1 

O'ahu Diverse Lowland Mesic Forest 2 G1 G1

Kaua'i Diverse Lowland Mesic Forest 2 G1 G1

Lana'i Diverse Lowland Mesic Forest 2 G1 G1

East Maui Diverse Montane Mesic Woodland 2 G1 G1

2 G1 G1

2 G1 G1

2 G1 G1

2 This forest association occurs only near sea level in a small area of the northeastern Olympic Peninsula and G1? G1 

1 G1G2Q G1

1 This open woodland association has been described from the eastern side of the Cascades Range, a mountG1 G1

2 This association occurs below 180 m (600 feet) elevation primarily in the northern portion of the Puget LowlaG1 G1 

2 This broad-leaved evergreen woodland association occurs in the southern Animas Valley in the "BorderlandsG1 G1

2 This is a deciduous woodland association found along lower treeline in the eastern Cascades near the ColumG1G2 G1

2 This is a deciduous riparian woodland association found below lower timberline in the eastern Cascades neaG1G2 G1

Oregon White Oak / Fescue Sparse Woodland2 This association is based on field observations and six releves. The association mostly occurs at lower conifG1? G1

1 This is a deciduous woodland association found along lower treeline in the eastern Cascades near the ColumG1G2 G1 

1 This forest association occurs only at low elevations in a small area of southwestern W G1 G1 ashington and adjace

2 This riparian woodland association is highly diverse floristically being on a transition zone between the MojavG1G2 G1

2 G1 G1

2 G1 G1

1 This forest association occurs primarily in the Puget Sound Basin in northwestern W G1G2 G1 ashington and adjacent 

1 This association occurs primarily on north-facing slopes of the San Juan Islands, and on easterly slopes of thG1G2 G1 

2 This association is found in bogs, primarily in the central and northern portion of the Puget Lowlands in W G1 G1 ash

2 This mid-seral to climax association occurs on perennially saturated or flooded peat soils adjacent to open mG1 G1

2 G1 G1

1 This linear forest plant community occurs on rich, moist high-bench floodplains of rivers that flood every five G2G3 G2

1 This small-patch coniferous forest community occurs on rocky headlands and beachplains along shorelines wG2G3 G2

1 This small-patch coniferous forest community occurs along the backshore of estuaries and tidal sloughs alonG2G3 G2

1 This matrix forest community occurs on zonal and near-zonal sites within the Coastal Douglas-fir moist maritG2 G2 

1 This matrix forest community occurs on a variety of mesic to submesic sites with medium to poor soil-nutrienG2G3 G2

Douglas-fir / Douglas Maple / Stepmoss Woodland 1 This small-patch plant community is restricted to mid and upper slope positions of steep south- and west-facG2 G2

1 This small-patch community occurs along the southern mainland coast and adjacent islands of British ColumG2G3 G2

1 This small-patch forest community occurs on rich, mesic or subhygric sites in coastal British Columbia at elevG2G3 G2

1 This community is found along the mainland coast adjacent to and sparingly on the northern half of VancouvG2G3 G2 
1 This closed-canopy forested community occurs at lower elevations on the south coast of British Columbia an

G2G3 G2 

1 This moist, submaritime coniferous community is found at higher elevations in drainages of the climatically trG2G3 G2

1 This moist maritime coniferous community is found along the leeward Vancouver Island Ranges from approxG2 G2 

1 This small-patch forest community occurs on rich circum-mesic sites in the Queen Charlotte Islands of British G2G3 G2

1 This community is distributed within the Southern Very Wet Hypermaritime Coastal W G1G3 G2 estern Hemlock Varian

m dryopteris Forest 1 This moist maritime coniferous community may be found roughly between 400 to 700 m above sea level alonG2 G2 

1 This coniferous forest community is found in the climatically transitional middle to leeward eastern valley sysG1G3 G2

1 This small- to large-patch forest community occurs on nutrient-poor, coarse sandy or skeletal soils on upper G2G3 G2

Balsam Fir - Red Spruce - Oatgrass - Peatmoss Swamp 1 This acidic conifer woodland or forested swamp occurs on moist to saturated soils in headwater basins in the G2 G2 

Balsam Fir - Red Spruce - Winterberry - Peatmoss Swamp 1 This acidic conifer woodland swamp occurs on temporarily to semipermanently flooded soils in frost-pocket hG2 G2 

Coastal Plain Calcareous Seepage Swamp 2 This calcareous seepage swamp occurs on the Virginia Coastal Plain on groundwater-saturated stream bottoG2 G2

Freshwater Tidal Woodland 2 This freshwater tidal woodland occurs on tidal rivers in Connecticut, Massachusetts, New York, and New JerG2 G2

Pine Barrens Riverside Shrub Savanna 2 This woody herbaceous community occurs in the Pine Barrens of New Jersey on the low terrace floodplains G2G3 G2

Atlantic White-cedar / Great Rhododendron Swamp 2 Saturated peatland forest dominated by <i>Chamaecyparis thyoides</i> with a dense shrub layer dominated G2G3 G2

Traprock Ridge 2 This traprock ridge open woodland is known from mountainous sites in New England, New Jersey, and PennG2G3 G2 

Red-cedar Rocky Summit 2 This calcareous rocky summit community occurs in New England and in the northeastern portion of the GreaG2G3 G2

Maritime Red-cedar Woodland 2 This maritime woodland community dominated by <i>Juniperus virginiana</i> occurs on sand dunes, upper eG2 G2

Swamp Forest - Bog Complex (Spruce Type) 2 This spruce-hemlock wetland forest of the central and southern Appalachian Mountains occurs on relatively fG2? G2

High Allegheny Red Spruce Peat Woodland 1 This acidic conifer woodland swamp occurs on saturated and temporarily flooded organic soils in headwater G2 G2 

Red Spruce / Heath / Peatmoss Woodland Swamp 1 This saturated acidic conifer woodland occurs in the Allegheny Mountains region of W G2G3 G2 est Virginia and easter

Red Spruce - Highbush Cranberry - Peatmoss High-Elevation Swamp 1 This acidic conifer woodland or forested swamp occurs on saturated and temporarily flooded soils in headwaG2 G2 

Mid-Successional Pine - Oak Woodland 2 This mid-successional pitch pine woodland occurs in the New Jersey Pine Barrens, with small outliers in New G2? G2 

Pine Barrens Pine - Oak Woodland 2 This pitch pine - oak woodland of dry sandy soils occurs in portions of the New Jersey Pine Barrens and the G2G3 G2

Coastal Pitch Pine Rocky Woodland 1 This pitch pine woodland community occurs primarily on near-coastal acidic rock outcrops of southern MaineG2 G2

Pitch Pine Dune Woodland 2 This maritime pitch pine woodland occurs on coastal sand dunes from southern Maine to Cape Henlopen, DG2G3 G2

New Jersey Pitch Pine / Scrub Oak Barrens 1 This pine barrens community is restricted to the New Jersey Pine Barrens. It is a highly fire-dependent commG2 G2

Coastal Plain Mesic Pine Barrens 2 Mesic pine barrens vegetation dominated by <i>Pinus rigida</i> with a shrub layer dominated by <i>Quercus G2? G2

Inland Pitch Pine / Scrub Oak Barrens 1 This pitch pine - scrub oak barren community occurs on northeastern sand plains, generally on outwash plaiG2 G2

Northern Pitch Pine / Scrub Oak Barrens 1 This northernmost pitch pine - scrub oak barren community occurs on flat glacial outwash plains. Soils are tyG2 G2

Dry River Bluff 2 This dry sandy riverbluff community occurs on the Merrimack and Soucook rivers in New Hampshire, and maG2 G2

Mid-Atlantic Coastal Maritime Forest 2 This mid-Atlantic coastal upland loblolly pine forest occurs on the Outer Coastal Plain and on barrier islands G2 G2

Central Appalachian / Piedmont Bedrock Floodplain W 2 This community is restricted to the Ridge and Valley and Piedmont sections of the Potomac River floodplain, oodland G2? G2

Sinkhole Pond Floodplain Forest 2 This sinkhole pond floodplain forest of northwestern New Jersey occurs in solution sinkholes that developed G2G3 G2

Successional Maritime Forest 2 This maritime forest community of the North Atlantic Coast Ecoregion occurs on sheltered backdunes, bluffsG2G3 G2

Ridge and Valley Dolomite Glade 2 This community type is a dolomite woodland of the Ridge and Valley of Virginia. It is physiognomically variabG2 G2

Piedmont / Coastal Plain Eastern Hemlock - Hardwood Forest 2 This association is known from steep, north-facing sites along rivers and large streams in the Piedmont, and G2G3 G2

Paper Birch / Hazel Forest 2 This paper birch / beaked hazelnut forest type is found in the northwestern Great Plains and Black Hills of thG2G3 G2

Paper Birch / Beaked Hazel Woodland 2 This paper birch / beaked hazelnut woodland is found in the northern Great Plains of the United States and CG2G3 G2

Beech - Hardwoods Till Plain Flatwoods 2 This community is found in the central midwestern United States and possibly adjacent Canada. Stands occG2G3 G2

Beech - Maple Glaciated Forest 1 This upland forest is found in the southern Great Lakes area of the United States and Canada. Stands occur G2G3 G2 

Beech - Mixed Hardwood Floodplain Forest 2 This beech - hardwoods floodplain forest community is found in the central United States and adjacent CanaG2G3 G2

Green Ash - Elm Woody Draw 2 This community type occurs in the northwestern Great Plains of the United States. Stands occur in upland raG2G3 G2

Central Tamarack - Red Maple Rich Swamp 2 This community is found in the central Great Lakes region, including southern Ontario, Canada and the northG2G3 G2

White Spruce / Twinflower Forest 1 This white spruce community type is known only from the Black Hills in the United States. It is on northwest- G2G3 G2

White Spruce Alluvial Black Hills Forest 1 The white spruce alluvial forest type is only known from the Black Hills of the United States. In the Hills, it is rG2G3 G2

Mixed Conifer / Common Juniper Alvar Woodland 1 The mixed conifer / common juniper alvar woodland type occurs scattered through the Great Lakes region in G2? G2

Shortleaf Pine / Little Bluestem Woodland 2 This shortleaf pine rock outcrop woodland type is found in the Interior Highlands region of the United States. G2G3 G2

White Pine - (Red Pine) Driftless Bluff Forest 2 This pine bluff forest occurs on steep sandstone or, rarely, limestone bluffs in the Driftless Area of the upper G2G3 G2

Driftless White Pine - Northern Hardwoods Forest 2 This pine-hardwoods community is found in the 'Driftless Region' of southeastern Minnesota, United States. G2? G2

Cottonwood / Switchgrass Floodplain Woodland2 This community is found in the central and southern Great Plains of the United States. Stands occur in floodpG2 G2 

Cottonwood / Western Snowberry Woodland 1 This riparian woodland community is found in the northwestern Great Plains of the United States on medium G2G3 G2 

White Oak - Post Oak / Bluestem Ozark Woodland 2 This white oak - post oak woodland community is found in the Ozarks and adjacent regions of the United StaG2G3 G2 
Lakeplain Mesic Oak Woodland 2 This community is found in the southern Great Lakes lakeplain of the United States and Canada, particularly 

G2 G2

Western Tallgrass Bur Oak Woodland 2 This bur oak woodland community is associated with the floodplains of rivers and streams in the central-wesG2G3 G2

Northwestern Great Plains Bur Oak Woodland2 This bur oak / beaked hazelnut is found in the north-central Great Plains of the United States and possibly adG2G3 G2

Bur Oak / Hophornbeam Forest 2 This bur oak community type is found in the Black Hills of the western United States. Stands occur at elevatiG2G3 G2

Chinquapin Oak - Bur Oak Ravine Woodland 2 This chinquapin oak - bur oak woodland community is found in the central tallgrass prairie region of the UniteG2 G2

Pin Oak - Post Oak Lowland Flatwoods 2 This pin oak - cherrybark oak bottomland or flatwoods forest community type is found in the central United SG2G3 G2

Northern (Great Lakes) Flatwoods 2 This pin oak - swamp white oak flatwoods is found in the midwestern United States and adjacent Canada neG2G3 G2

Pin Oak - Swamp White Oak Sand Flatwoods 2 This pin oak - swamp white oak sand flatwoods community is found in the midwestern United States and adjG2? G2

Post Oak - Blackjack Oak / Bluestem Sand Woodland 2 This post oak - blackjack oak woodland community is found in the alluvial sand terraces of the Upper MississG2 G2 

Ozark/Ouachita Post Oak - Blackjack Oak / Little Bluestem W 2 This post oak - blackjack oak woodland type occurs in the central United States, particularly in the Interior Looodland G2G3 G2

Post Oak Flatwoods 2 This dry post oak flatwoods type is found in the central midwestern United States. Stands occur on both glacG2G3 G2

Northern White-cedar - Yellow Birch Forest 2 This upland white-cedar - hardwood forest is found in the northern Great Lakes region of the United States aG2Q G2

Appalachian Cliff White-cedar Woodland 2 This white-cedar cliff woodland type is found in the Appalachian and Allegheny Plateau region of the United G2G3 G2

Hemlock - Sugar Maple Relict Forest 2 This hemlock forest type occurs in the 'Driftless Region' of southern W G2 isconsin, of the United States. Stands G2 

West Gulf Coastal Plain Xeric Post Oak Woodland 2 This woodland occurs on narrow, topographically isolated, convex ridgetops and interstream divides in the W G2 G2 

West Gulf Coastal Plain Dry Post Oak Woodland 2 This woodland occurs on narrow, topographically isolated, convex ridgetops and interstream divides on the W G2 G2 

Sandhill/Pocosin Ecotone 1 This community occurs in narrow bands between various sandhill communities and streamhead pocosins, in G2 G2

Mesic Mixed Mount Magazine Forest 2 This association is known from moist, north-facing, calcareous lower slopes of Mount Magazine (Arkansas RG2 G2

Southern Edwards Plateau Bigtooth Maple Canyon Forest 2 This association includes mesic canyon forests of the southern Edwards Plateau, from Kendall County west G2 G2

2 This forest occurs in the most mesic canyons of the Guadalupe Mountains in the Trans-Pecos of Texas. It is G2? G2

Piedmont Streamside Seepage Swamp 2 This streamside seepage vegetation is found in the southeastern Piedmont of North Carolina. It occurs along G2G3 G2

Sandstone Seepage Forest/Woodland 2 This acidic seepage forest community occurs on nearly level sandstone plateaus of Mount Magazine, ArkansG2? G2

Interior Forested Acidic Seep 2 This forested acid seep occurs at the base of steep to moderate slopes where water percolates out through CG2G3 G2 

Cumberland Open Acidic Seep 2 This association includes open acid seeps found on broad sandstone ridges in the Appalachian Plateau of KG2G3 G2 

a flava) Woodland 2 Seasonally saturated, open-canopied, acid seeps in the Uwharrie Mountains portion of the Piedmont of North G2 G2

Cayur - Mangle Boton / Acrostichum Bosque 1 G2G3 G2

1 This community occurs in most of the ranges of the Trans-Pecos; composition differs from range to range. AG2? G2

Southern Appalachian Hardwood Rich Boulderfield Forest 1 This association includes boulderfield forests of the southern Appalachians, with abundant <i>Betula alleghaG2G3 G2

Southern Appalachian Boulderfield Forest (Currant and Rockcap Fern Type) 1 This association includes high-elevation boulderfield forests of the southern Appalachians, strongly dominateG2G3 G2 

Central Appalachian High-Elevation Boulderfield Forest 2 This community is known from high elevations of the northern Blue Ridge, Ridge and Valley, and Allegheny MG2 G2 

Montane Basic Hardwood - (Red-cedar) Woodland 2 These montane woodlands of the Southern Blue Ridge are currently known from the lower mountains of NorG2 G2

Blue Ridge Calcareous Shale Slope Woodland (Shrubby Type) 2 These deciduous or mostly deciduous edaphically maintained woodlands are known from the Southern Blue G2 G2

Pignut Hickory - Southern Basswood - Southern Sugar Maple / Mottled Trillium Forest 2 This association is a mesic to dry-mesic forest occurring on calcareous or other base-rich or circumneutral soG2G3 G2

Gulf Coastal Plain Catalpa - Willow Forest 2 This sandbar community occurs along small rivers and large creeks in the Red Hills of Alabama (East Gulf CG2G3 G2

Sandhills Atlantic White-cedar Streamside Forest 1 This forest, found along streams or at seepages in the Fall-line Sandhills, is usually dominated by <i>ChamaG2 G2

Gulf Coastal Plain White-cedar Swamp 2 This forest is dominated by a mixed <i>Chamaecyparis thyoides - Pinus elliottii var. elliottii</i> canopy which G2 G2

Central Florida Atlantic White-cedar Hydric Hammock 1 This association includes hydric hammock forests found in the central peninsula of Florida. These forests are G2 G2

Steephead White-cedar Woodland 1 This community is associated with "steephead streams" in the Florida Panhandle and adjacent Alabama, and G2? G2 

Gulf Coastal Plain Streamside White-cedar Swamp 1 This association, of the East Gulf Coastal Plain of Florida, Alabama, and Mississippi, occurs along small blacG2G3 G2

Peatland Atlantic White-cedar Forest 2 <i>Chamaecyparis thyoides / Persea palustris / Lyonia lucida - Ilex coriacea</i> Forest is found in flat, non-aG2 G2 

1 This community is a short woodland or tall shrubland community of subtropical Florida, with canopy height raG2 G2

Eastern Mayhaw Pond 1 This community occurs in sinkholes and other isolated upland depressions of the South Atlantic and East GuG2G3 G2

Rufous Mayhaw Pond 1 This association accommodates isolated seasonal depression ponds dominated by <i>Crataegus rufula</i>, G2G3 G2

West Gulf Coastal Plain Beech - Magnolia Forest 1 This West Gulf Coastal Plain beech-magnolia forest displays a well-developed three-layered structure; a closG2 G2

2 This association includes beech-magnolia forests of small perennial stream bottoms within the range of <i>PG2G3 G2

Atlantic Coastal Plain Acidic Loam Beech - Magnolia Forest 1 This forest occurs in ravines, protected coves, and sometimes on broad upland flats protected from fire in the G2G3 G2

Red Hills Beech - Magnolia Forest 1 This is a generally circumneutral beech - magnolia association which occurs on slopes in the Alabama Red HG2? G2

Woodville Karst Plain Hardwood Forest 1 This mixed mesic forest is found between the lower Wakulla River and the St. Marks River, over large flat areG2G3 G2 

Gulf Coastal Plain Loess Bluff Beech - Oak Forest (Northern Type) 2 This forest, dominated by <i>Fagus grandifolia</i> and <i>Quercus </i>spp., occurs on deep loess soils in thG2G3 G2

West Gulf Coastal Plain Beech - White Oak Forest (Subcalcareous Type) 2 This mesic, subcalcareous forest of the West Gulf Coastal Plain of eastern Texas and western Louisiana is tG2G3 G2 

Piedmont Beech / Heath Bluff 2 This association includes heath bluffs on steep north-facing slopes in the lower Piedmont and upper Coastal G2G3 G2

Central Appalachian Basic Woodland 2 This association is a woodland dominated by <i>Fraxinus americana</i> and <i>Carya glabra</i>, occurring G2 G2 
Piedmont Granitic Dome Woodland (Basic Type) 2 Woodlands dominated by <i>Fraxinus americana</i> and <i>Carya glabra</i>, occurring in nutrient-rich soils 

G2 G2

2 This association is a mesic to dry-mesic calcareous forest occurring over limestone in the Florida PanhandleG2 G2

Tropical/Subtropical Popash Slough 1 This type is restricted to tropical/subtropical southern Florida. <i>Fraxinus caroliniana</i> is the dominant treG2G3 G2

West Gulf Coastal Plain Carolina Ash Swamp 2 This wetland depression of the West Gulf Coastal Plain is typified by a nearly monospecific, dense stand of <G2G3 G2

Columbia Bottomlands Ash Flat 2 This community occupies shallow depressions on Vertisols that exhibit strong gilgai microtopography. The soG2? G2

Macon Ridge Green Ash Pond 2 This association is only known from ponds on Macon Ridge in the Mississippi River Alluvial Plain of northeasG2? G2

Atlantic Coastal Plain Green Ash Slough Forest2 This forest occurs on somewhat poorly drained to poorly drained silty clay loam soils in temporarily flooded sG2G3 G2

Eastern Knobs Ledge/Cliff Glade Woodland 2 This community occurs on Mississippian limestones of the Eastern Knobs and Mississippian Plateaus regionG2 G2

2 This community is a saturated forest dominated by <i>Gordonia lasianthus</i>. Other trees present in the caG2G3 G2 

1 <i>Juniperus ashei</i> woodlands in the Arbuckle Mountains of Oklahoma (Johnston, Marshall, Murray, and G2G3 G2

Ozark Ashe's Juniper Glade Woodland 1 This community is found in the Ozarks region of the United States. It occurs on gently sloping exposures of dG2? G2

Ozark Ashe's Juniper Clifftop Woodland 1 This association includes <i>Juniperus ashei</i> woodlands occurring on rimrock bluffs and cliffs composed G2? G2

South Atlantic Coastal Shell Midden Woodland2 This calciphilic community occurs on calcareous coastal sands, shell hashes, Amerindian shell middens, and G2? G2

Black Belt Prairie Cedar Woodland 2 This short-stature forest of the Black Belt of Alabama and Mississippi has a typically closed canopy, usually sG2 G2

Bluegrass Ledge/Cliff Glade Woodland 2 This community occurs on Middle Ordovician Limestone of the Inner Bluegrass region of Kentucky. The canoG2 G2 

2 This community occurs as small (less than one acre) depressions scattered in low oak flats in the Outer CoaG2G3 G2 

2 This <i>Maclura pomifera</i>-dominated riparian mesic blackland community occurs in deep soils on level teG2? G2 

East Gulf Coastal Plain Western Bayhead 2 This plant association comprises small ravine-bottom seepage-fed bayheads of the western part of the East G2G3 G2 

Florida Panhandle Steephead Seepage Forest2 Stands of this association are seepage-fed saturated forests found at the base of steepheads and the upper G2 G2

Lower Keys Rockland Hammock 1 This community is a low (4-7 m in height), xeric forest with occasional emergent trees, occurring over limestoG2 G2

Upper Keys Rockland Hammock 1 This community is a dense, tropical, broad-leaved, evergreen forest with an open understory, occurring on aG2 G2 

Swamp Blackgum Floodplain Seepage Forest2 This community occurs in floodplain edges of brownwater floodplains in the South Atlantic and Mid-Atlantic CG2G3 G2 

a alnifolia Forest 2 This nonriverine swamp forest of the mid-Atlantic Coastal Plain has a closed canopy dominated by <i>Nyssa G2 G2

West Gulf Coastal Plain High Terrace Wooded Flatwoods Pond 2 This community type occurs in isolated ponds in a longleaf pine landscape in the high Pleistocene terraces oG2? G2

Nonriverine Swamp Forest (Sweetgum Type) 2 In this nonriverine swamp forest, <i>Liquidambar styraciflua, Nyssa biflora</i>, and <i>Acer rubrum var. trilobG2? G2

2 These saturated forests occur in seepage-influenced areas adjacent to small streams in southern portions of G2G3 G2

St. Marks Freshwater Tidal Swamp Forest 2 This association represents one of several freshwater tidal swamp forests found in the Florida portion of the G2 G2

Lafayette-type Freshwater Tidal Swamp Forest2 This association represents one of several freshwater tidal swamp forests found in the Florida portion of the G2 G2

East Gulf Coastal Plain Blackgum Dome Swamp2 This dome swamp community occurs in the East Gulf Coastal Plain of Florida and Alabama and the South AG2G3 G2 

Sandhills Ogeechee Tupelo Depression 2 This association is dominated by <i>Nyssa ogeche</i>, with some <i>Nyssa biflora</i> and <i>Acer rubrum<G2? G2

South Atlantic Coastal Plain Flatwoods Ogeechee Tupelo Pond 2 Depressional sinkhole wetlands dominated by <i>Nyssa ogeche</i>, occurring in a matrix of pine flatwoods, G2? G2 

Red Spruce - Fraser Fir Forest (Deciduous Shrub Type) 1 This community is restricted to the highest mountain systems of the southern Appalachians in eastern TenneG2 G2

Red Spruce - Northern Hardwood Forest (Herb Type) 1 This association occurs in the broad elevational transition zone between spruce-fir and northern hardwoods G2 G2

Red Spruce Forest (Protected Slope Type) 1 This association includes moist slope forests of the central and southern Appalachians. <i>Abies fraseri</i> G2G3 G2 

Red Spruce Forest (Central Appalachian Upland Type) 1 This association occurs on both gentle slopes bordering high-elevation valley floors and on more exposed ridG2 G2 

1 Stands of this association occur on canyon slopes at high elevations (above 5000 feet) in the Chisos MountaG2? G2

1 This community occurs at moderate to high elevations in the Chisos Mountains, in relatively moist situations. G2? G2

1 This community occurs in lower to moderate elevations in the Chisos Mountains of Trans-Pecos Texas. It maG2? G2

1 This Mexican pinyon - oak community type occurs at relatively low-elevation valleys and flats in the Davis MoG2? G2

1 This is a very dry <i>Pinus cembroides - Quercus grisea</i> woodland, occurring on igneous rock in the ChisG2? G2

1 Higher elevations in the Davis Mountains. G2? G2

Peninsular Sand Pine Forest 2 This closed-canopy forest occurs in the Florida peninsula. The canopy (10-20 m high) is composed of <i>PinG2 G2

Panhandle Sand Pine Dune Scrub 1 <i>Pinus clausa (= var. immuginata)</i> dominates the open and variable canopy of this scrub association. <G2 G2

Inland Sand Pine Scrub 1 This inland peninsular scrub consists of a low-statured, emergent <i>Pinus clausa</i> canopy over a dense sG2 G2

Upper Piedmont Mafic Shortleaf Pine - Oak W2oodland This Upper Piedmont association occurs on moderate to steep slopes over soils derived from mafic rock. BeG2? G2

West Gulf Coastal Plain Shortleaf - Loblolly - Mixed Oak Forest 2 This forest association of the West Gulf Coastal Plain and Upper W G2G3est Gulf Coastal Plain ecoregions is codoG2

West Gulf Coastal Plain Xeric Upland Shortleaf Pine - Oak W 2 This shortleaf pine-oak forest/woodland occurs on xeric sandy uplands west of the Mississippi River in the Uoodland G2 G2 

oneuron album Woodland 2 This mixed evergreen - deciduous sparse forest association consists of prairie-like woodlands occurring over G2 G2

West Gulf Coastal Plain Shortleaf Pine - Oak Rich Mesic Forest 2 This mesic to dry-mesic forest of the West Gulf Coastal Plain is typified by an overstory of both <i>Pinus echG2G3 G2

Piedmont Pine - Oak Heath Bluff 2 This Piedmont woodland occurs on upper slopes, often west-facing, with extreme exposure that results in exG2? G2

Pine-Oak Virginia Shield Barrens 2 'Shield barrens' of sandstone areas in southwestern Virginia. These are fire-maintained shortleaf pine - oak wG2? G2

Ozark/Ouachita Shortleaf Pine - Oak Dry Woodland 1 This shortleaf pine - oak woodland is found in the Ozark/Ouachita region of the United States. Stands occur G2G3 G2
West Gulf Coastal Plain Xeric Stream Terrace Shortleaf Pine W 2 This xeric stream terrace forest/woodland of the W oodland est Gulf Coastal Plain occurs on very well-drained Pleisto

G2Q G2

East Gulf Coastal Plain Blackwater Levee Forest 2 This association is documented from a high sandy levee in the Styx River, Baldwin County, Alabama. It is a tG2 G2

Central Florida Slash Pine Flatwoods 2 This community is restricted to the central Florida peninsula. Stands have canopies dominated by <i>Pinus eG2? G2

Big Cypress Palm Pine Rockland 2 Upland <i>Pinus elliottii var. densa</i>-dominated vegetation of southern Florida. Occurrences may be floodG2? G2

Big Cypress Coco-plum - Dahoon Pine Rockland2 G2? G2

Maritime Slash Pine Upland Flatwoods 1 This maritime-influenced, upland <i>Pinus elliottii var. elliottii</i> woodland occurs on barrier islands and neaG2G3 G2

minor, psittacina) Woodland 1 These are slash pine flatwoods of the lower East Gulf Coastal Plain, with open canopy of <i>Pinus elliottii vaG2? G2

East Gulf Coastal Plain Slash Pine Bayhead Swamp 2 This bayhead community of the East Gulf Coastal Plain has a closed canopy (or nearly so) of <i>Pinus elliottG2G3 G2 

South Atlantic Wet Slash Pine Flatwoods 2 This wet flatwoods of the South Atlantic Coastal Plain in Georgia is typified by a canopy which ranges from oG2? G2

Gulf Coast Wet Slash Pine Flatwoods 2 This wet flatwoods of the western portion of the East Gulf Coastal Plain has a mixed canopy characterized bG2? G2

East Gulf Coastal Plain Slash Pine - Titi Swamp1 This association presumably represents swamps of the East Gulf Coastal Plain of Florida (and possibly MissG2G3Q G2

South Atlantic Swamp Island 2 This community occurs on isolated ridges surrounded by swamps in the floodplains of large Coastal Plain rivG2G3 G2

Peninsular Florida Scrubby Flatwoods 2 This scrubby flatwoods association of the southern peninsula of Florida is typified by an open to very open caG2G3 G2

1 This pine flatwoods community occurs in eastern Georgia. The open (to fairly closed) canopy is characterizeG2 G2

Wet Longleaf Pine Flatwoods (Northern Type)1 <i>Pinus palustris</i> (and sometimes <i>Pinus taeda</i> or <i>Pinus serotina</i>) dominates the open canG2 G2

West Gulf Coastal Plain Fire-Infrequent Mixed Longleaf Pine Forest/W 2 This sandy upland <i>Pinus palustris</i> woodland of the W oodland est Gulf Coastal Plain occurs on topographically G2G3 G2

East Gulf Coastal Plain Lorman Soil Longleaf Pine W 1 This longleaf pine woodland is described from the hilly and ruggedly dissected uplands of the Homochitto Naoodland G2G3 G2

Montane Mixed Longleaf Woodland 1 This is one of several associations representing longleaf pine stands of interior regions of the southeastern UG2 G2

1 This association occurs on Leon soils on barrier islands, with 30-40% pine cover and 100% shrubby oak covG2? G2

Atlantic Coastal Plain Wet Ultisol Longleaf Pine Savanna 1 This saturated longleaf pine - pond pine woodland association is restricted to wet and moist Ultisols of the AtG2 G2

Carolina Coastal Longleaf Pine Sandhill 1 This community occurs on xeric sands within several miles of the coast in southeastern North Carolina and SG2 G2

West Gulf Coastal Plain Clayey Longleaf Pine Forest 2 This upland <i>Pinus palustris</i> woodland of the West Gulf Coastal Plain occurs in limited areas primarily G2G3 G2

Atlantic Coastal Plain Mesic Longleaf Woodland1 This is a mesic longleaf pine community, without scrub oaks, occurring on mesic soils in the middle and outeG2G3 G2 

Fall-line Mesic Longleaf Pine Woodland 1 This is a mesic longleaf pine community, without scrub oaks (or with very few individuals of <i>Quercus mariG2G3 G2 

West Gulf Coastal Plain Wet Longleaf Pine Savanna (High Terraces Type) 1 This is a saturated longleaf pine woodland community of central to west-central Louisiana, presumably rangiG2G3 G2

Wet Pine Flatwoods (Leiophyllum Type) 1 This community is very restricted in range, occurring only in Brunswick County, North Carolina, where it is thG2? G2

Munson Sandhill, Bluejack Oak Phase 2 This <i>Pinus palustris</i>-dominated community occurs on dry, sandy, well-drained soils in the East Gulf CoG2? G2

Central Florida Longleaf Island 1 This central Florida sandhill is dominated by an open canopy of <i>Pinus palustris</i>. This community typicG2 G2

West Gulf Coastal Plain Xeric Longleaf Pine Sandhill 1 This xeric woodland of the West Gulf Coastal Plain is dominated by an open to fairly closed <i>Pinus palustrG2G3 G2 

South Atlantic Sandhills Subxeric Longleaf Pine W1 This association occurs in subxeric habitats of the sandhills and inner South Atlantic Coastal Plain of eastern oodland G2G3 G2

1 This association occurs in eastern Georgia on sandy loam soils. <i>Pinus palustris</i> forms an open to closG2G3 G2

1 This association occurs in sandhill landscapes of North Carolina and South Carolina and is found more mesiG2G3 G2 

West Gulf Coastal Plain Subxeric Longleaf Pine Sandhill 1 This subxeric woodland of the West Gulf Coastal Plain is dominated by an open to fairly closed <i>Pinus palG2G3 G2

South Carolina Central Longleaf Woodland 1 This association of the Fall-line Sandhills region of South Carolina has an open canopy dominated by <i>PinG2 G2

Atlantic Coastal Fringe Longleaf Sandhill Scrub1 These are xeric longleaf pine sandhills, occurring in the Outer Coastal Plain of North Carolina and South CarG2? G2 

South Atlantic Xeric Longleaf Pine Sandhill 1 This association occurs in the xeric habitats of the sandhills and inner South Atlantic Coastal Plain of eastern G2G3 G2

Atlantic Coastal Plain Xeric Sandhill Scrub 1 These are extremely xeric longleaf pine sandhills, typically with a very sparse <i>Pinus palustris</i> canopy G2 G2

1 This is one of the driest longleaf pine types on the Atlantic Coastal Plain, north of central South Carolina. It is G2G3 G2

1 To be added from North Carolina Vegetation Survey data. G2G3 G2

East Gulf Coastal Plain Subxeric Longleaf Pine Sandhill 1 This East Gulf Coastal Plain community is characterized by a canopy of widely spaced <i>Pinus palustris</i> G2 G2

South Atlantic Coastal Plain Dry Longleaf Pine Sandhill 2 This sandhill community occurs on dry, sandy, well-drained soils in the Coastal Plain of eastern Georgia and G2G3 G2

2 Sandhill community of the East Gulf Coastal Plain, occurring on deep, excessively drained white sand soils, G2 G2

2 This is a subxeric <i>Pinus palustris</i>-dominated woodland of the Outer Coastal Plain of South Carolina, fG2? G2

Altamaha Grit Longleaf Pine Woodland 1 This community is known from Broxton Rocks in south-central Georgia (Coffee County); it is a characteristic G2 G2

Atlantic Longleaf Pine - Blackjack Oak Woodland 1 This longleaf pine/scrub oak association is distributed primarily in the Fall-line Sandhills of south-central NortG2G3 G2

West Gulf Coastal Plain Clayey Longleaf Pine W1 This W oodland (Dry Type) est Gulf Coastal Plain woodland is comprised of an open to very open, typically somewhat stunted, <G2 G2

West Gulf Coastal Plain Clayey Longleaf Pine W1 This W oodland (Moist Type) est Gulf Coastal Plain association is comprised of an open to very open, typically stunted, <i>Pinus paG2 G2

Mississippi Loam Hills Longleaf Forest 1 This association occurs on rolling upland hills, on ridges and slopes of all exposures and slopes, but is more G2G3 G2

Fall-line Sandhills Longleaf Pine - Blackjack Oak W 1 This community occupies topographically high positions in the Fall-line Sandhills of North Carolina and South oodland G2? G2

2 This is the drier portion of the longleaf pine woodlands of the South Carolina "wiregrass gap" with <i>QuercuG2? G2

1 This association is an upland longleaf pine community occurring in the East Gulf Coastal Plain on well-draineG2G3 G2

Western Wet Longleaf Pine Savanna (Prairie Terraces Acidic Silt Loam Type) 1 This is apparently the southernmost wetland longleaf community of the W G2G3 est Gulf Coastal Plain, occurring oG2
Western East Gulf Coastal Plain Silt Loam Longleaf Pine W 1 This association occurs on finer-textured, loess-influenced soils in eastern Louisiana and is likely also in adja

oodland G2 G2

West Gulf Coastal Plain Mesic Upland Longleaf Pine W 1 This mesic longleaf pine woodland occurs in the W oodland est Gulf Coastal Plain. It is dominated by a generally open G2G3 G2

Florida Parishes Coastal Terrace Longleaf Pine Flatwoods 1 This association occurs on upland rises in the lowest terrace of coastal flatwoods in the Florida parishes of LG2? G2

West Gulf Coastal Plain Dry-Mesic Upland Longleaf Pine W 1 This dry-mesic longleaf pine woodland of the W oodland est Gulf Coastal Plain is dominated by a 20- to 25-m tall <i>PG2G3 G2

Western Upland Longleaf Pine Forest (Messer Pimple Mound Type) 1 This mesic <i>Pinus palustris</i> woodland of the West Gulf Coastal Plain occurs on pimple mounds of the PG2 G2 

Longleaf Pine / Saw Palmetto Flatwoods 1 This broadly defined community is a moderately to poorly drained longleaf flatwoods community, widespread G2G3 G2

South Atlantic Coastal Plain Longleaf Flatwoods1 This <i>Pinus palustris</i> flatwoods community is found in the South Atlantic Coastal Plain of northeastern G2G3 G2

2 This forest occurs at high elevations in the mountain ranges of Trans-Pecos Texas. Dominant canopy specieG2? G2

Papershell Pinyon - Ashe Juniper Woodland 2 This community occurs in the Edwards Plateau of central Texas. The open canopy consists of <i>Pinus remoG2G3 G2

2 This community occurs at moderate elevations in the Sierra Madera of Trans-Pecos Texas. <i>Pinus remotaG2G3 G2

Blue Ridge Table Mountain Pine - Pitch Pine W1oodland (High-Elevation Type) This high-elevation (1220 to 1555 m [4000-5100 feet]) woodland is dominated by <i>Pinus rigida</i> with a dG2 G2 

Hi Lewis Pitch Pine Barrens 2 This association includes dry woodlands of the Cumberlands of Kentucky and possibly Virginia on steep, souG2? G2

Small Depression Pocosin 1 Small Depression Pocosins occurring in small depressions in sandy upland landscapes, differing in floristic cG2G3 G2

Central Florida Pond Pine Shrubby Flatwoods 1 These are wet flatwoods of <i>Pinus serotina</i> with a small amount of <i>Pinus elliottii</i>. The shrubs <i>G2G3 G2

1 <i>Pinus serotina</i> is dominant or codominant with <i>Acer rubrum</i> in the canopy stratum. <i>Acer rubG2? G2 

Pond Pine Peat Dome Pocosin (Strange Nutrient-rich/Tidal? Type) 1 This natural community is found on the margins of large peat domes and with some tidal or nutrient-rich grouG2? G2 

East Gulf Coastal Plain Pond Pine / Herbaceous W 1 These are linear pond pine woodlands occurring along seepage-fed transition zones in the Florida Panhandloodland G2 G2

Southern Appalachian White Pine Forest 1 This association includes natural stands of forest vegetation with a canopy dominated by <i>Pinus strobus</G2G3 G2

West Gulf Coastal Plain Subcalcareous Pine - Hardwood Slope and Stream Bottom Forest 2 This mixed forest of the West Gulf Coastal Plain occurs in a fairly narrow geographic zone on both sides of tG2G3 G2

2 This type includes nonriverine swamps of the Outer Coastal Plain (embayed or tidewater region) of North CaG2G3 G2

Wind-Tidal Cypress - Gum Swamp 2 This community occurs on relatively firm, poorly decomposed, fibrous and root-rich peat, which usually overlG2? G2

Loblolly Pine - Sand Laurel Oak Woodland 2 This community consists of pine-oak woodlands on sandy swamp islands isolated from fire, or on levees and G2 G2

Atlantic Coastal Plain Loblolly Pine - Oak - Atlantic W 2 These forests occur along sandy blackwater streams, and on low, sandy terraces and levees, on the Atlantic hite-cedar Blackwater Stream Forest G2? G2

Blue Ridge Acidic Shale Woodland 2 This community occurs on steep, shaly slopes in the southern Appalachians and has an open to closed, stunG2 G2 

Appalachian Montane Alluvial Forest 2 This association covers alluvial forests of Southern Blue Ridge and nearby portions of the inner Piedmont. TG2? G2

Coastal Mesquite / Cactus Woodland 2 This woodland occurs on upland (but subirrigated) saline soils near the coast of southern Texas. <i>Prosopis G2? G2

Tamaulipan Mesquite Brushland 2 This deciduous woodland association occurs on non-saline, coarse- and fine-textured Beaumont Formation sG2? G2

Southeastern Highland Rim Blackjack Oak Barrens 2 This woodland occurs on flat dry uplands of the southeastern Highland Rim in Tennessee. The open canopy G2G3 G2

Southern Ridge and Valley Calcareous Flatwoods Forest 2 These seasonally inundated wet hardwood forests occur on gently rolling or flat terrain along small streams aG2? G2

Chesapeake Bay Nonriverine Wet Hardwood Forest 2 This association occurs in the central and northern Virginia Coastal Plain on extensive, flat terraces and very G2? G2

Piedmont Rocky Mafic Forest 2 This forest occurs on mafic rocky soils with some occurrences in Piedmont "boulder gardens." There are areG2? G2

Appalachian Montane Oak-Hickory Forest (Low-Elevation Xeric Type) 2 This association includes dry, deciduous forests of low elevations (below 915 m [3000 feet]) in the Southern G2G3 G2

Upper West Gulf Coastal Plain Subcalcareous W2 This community occurs on mesic, circumneutral slopes in eastern Texas. The canopy is dominated by <i>Quhite Oak - Dwarf Palmetto Forest G2G3 G2

Piedmont Rocky Mesic Mafic Forest 2 This Piedmont forest often occurs in moderately protected situations on lower slopes of escarpments, on alluG2G3Q G2

Piedmont Mafic Dry Oak - Hickory Forest (Post Oak Type) 2 This Piedmont forest occurs on soils derived from mafic rocks, in the Carolina Slate Belt and possibly elsewhG2G3 G2

West Gulf Coastal Plain Subcalcareous White Oak Forest 2 This <i>Quercus alba</i>-dominated forest occurs on steep, moist slopes, over slightly calcareous or subcalG2? G2

Southern Blue Ridge High-Elevation White Oak Forest 2 This community comprises <i>Quercus alba</i>-dominated forests on exposed, rocky ridges and convex uppG2Q G2

Upper West Gulf Coastal Plain Xeric Sandhill Complex (Arkansas Oak Type) 2 This xeric woodland is characterized by a low (<12 m), open canopy often dominated by <i>Quercus arkansaG2 G2 

Arbuckle Mountain Texas Oak Forest 1 This forest occurs on xeric to mesic rocky slopes over conglomerate or limestone in the Arbuckle Mountains G2G3 G2

Atlantic Coast Calcareous Fringe Hardwood Forest 2 This community is a mid-Atlantic near-coastal forest that occurs on the North Carolina and South Carolina mG2G3 G2 

Southern Red Oak Flatwoods Forest 2 This southern red oak flatwoods forest is found in parts of the Interior Low Plateau and adjacent areas of the G2? G2

2 This woodland is stunted (2-15 feet tall) and occurs on the rocky granite slopes of Quartz Mountain (northweG2? G2 

Texas Coastal Bend Live Oak - Redbay Forest1 The natural forms of this community consist of closed to open canopy <i>Quercus fusiformis</i> [see commeG2? G2

Southeastern Florida Maritime Hammock 1 This association represents xeric maritime hammocks of the central eastern coast of Florida and adjacent arG2? G2

Lake Wales Ridge Xeric Hammock 1 This association occurs on xeric hammocks of Florida's Lake WG2G3 ales Ridge on deep coarse sands. These forG2

1 Xeric maritime hammocks of the panhandle of Florida and possibly adjacent Alabama. G2? G2

Northern Gulf Xeric Hammock 2 This is a poorly understood and documented hardwood association found in the outer portions of the East GG2G3? G2 

Central Florida Sand Laurel Oak Hammock 2 These are dry-mesic to xeric hammocks of central Florida dominated by <i>Quercus hemisphaerica, Carya gG2? G2

Florida Steephead Forest 2 These forests occur on steep slopes of steepheads and spring-run streams of the Florida Panhandle. The caG2G3 G2

Atlantic Coastal Plain Swamp Island Forest 2 This association is found on swamp islands in the outer and middle Coastal Plain of North Carolina, South CG2G3 G2

Sand Laurel Oak - Sand Live Oak Hammock 2 This forest occurs on fire-protected islands of high ground surrounded by riverine swamps, and on slopes anG2G3 G2

Lacey Oak - Ashe's Juniper Woodland 2 This woodland is dominated by <i>Quercus laceyi</i> and <i>Juniperus ashei</i>. The canopy is 6-12 m higG2 G2
East Gulf Coastal Plain Blackgum Bayhead Forest (Clayey Type) 2 This saturated forest association is found in the East Gulf Coastal Plain from Louisiana to Alabama in bayhea

G2? G2 

2 This forest occurs in wetter sloughs associated with <i>~Quercus michauxii - Quercus pagoda / Clethra alnifoG2G3 G2 

Interior Oak - Swamp Cottonwood Pond Forest2 This upland swamp association is found in the Highland Rim (Pennyroyal Karst Plain) of Tennessee and KenG2G3 G2

Mixed Oak - Hardwood Sand Pond Forest 2 This mixed oak - hardwood sand pond forest is found in the western edge of the Mississippi River Alluvial PlaG2? G2 

Red River Pimplemound Terrace Depression Oak Forest 2 This community occurs in seasonally flooded depressions in old meander scars on second terraces of ancieG2G3 G2

Overcup Oak Pond Forest 2 This overcup oak pond forest is found in the south-central United States in southern Missouri and Arkansas. G1G3 G2 

Western Highland Rim Blackjack Oak Barrens2 These barrens are found on flat exposed ridgetops of the Western Highland Rim (Lewis County, Tennessee)G2 G2

2 This association is a hardwood - loblolly pine forest found in Louisiana's East Gulf Coastal Plain on flats of thG2G3 G2

2 This forest occurs on extensive interstream flats with fine-textured mineral soils. Hydrology is seasonally to nG2 G2

2 This forest community occurs on the edges of brownwater floodplains in the Atlantic Coastal Plain, in situatioG2G3 G2

Chinquapin Oak Unglaciated Bluff Woodland 2 This chinquapin oak bluff woodland occurs primarily on bluffs of rivers in the southern unglaciated Interior LoG2G3 G2

South Atlantic Coastal Plain Limestone Forest2 This mesic, calcareous oak-hickory forest is known from the Atlantic Coastal Plain of Georgia in sheltered sitG2 G2

Edwards Plateau Moist Limestone Slope Forest2 This association occurs on mesic limestone slopes in the Edwards Plateau of Texas. <i>Quercus muehlenbeG2G3 G2

1 This type includes evergreen oak hammocks of Florida Panhandle riverbanks that are dominated by <i>QueG2? G2

Atlantic Coastal Plain Mesic Cherrybark Oak - Hickory Forest 2 This mesic forest or woodland is described from the South Carolina Coastal Plain. It is associated with soils G2? G2

Louisiana East Gulf Coastal Plain Pleistocene Prairie Terrace Forest 2 This is a loess forest of the essentially flat to very gently rolling Pleistocene Prairie Terraces of Baton RougeG2? G2

nthium laxum Forest 2 This oak flat forest occurs on moist to wet flats in interstream divides in regions of very subdued topographic G2? G2

Piedmont Triassic Basin Oak Bottomland Forest 2 This association covers Piedmont bottomland forests which occur in broad, flat floodplains of Triassic basinsG2? G2

Pin Oak - Swamp White Oak Seasonal Pond 2 This wetland forest community is nearly endemic to hardpan soils of the Culpeper Basin in northern Virginia G2 G2

Ozark Pin Oak Pond Forest 2 This association includes small, isolated, <i>Quercus palustris</i>-dominated seasonally flooded ponds in upG2 G2

Highland Rim Barrens Depression Willow Oak Forest 2 This association encompasses forests of poorly drained shallow upland depressions on very flat landscapes G2 G2

West Gulf Coastal Plain Oak / Dwarf Palmetto Rich Bottomland Forest 2 This oak-palmetto bottomland forest is found in limited areas in the W G2G3 est Gulf Coastal Plain. Possibly the moG2

Atlantic Upland Depression Willow Oak Swamp Forest 2 This association represents upland depression swamps found in the Piedmont of the Carolinas, Virginia, and G2G3 G2

Mafic Xeric Piedmont Oak Forest 2 This is an oak-hickory forest of the Piedmont which is found on various mafic volcanic substrates, including aG2? G2

2 This woodland is apparently restricted to xeric sandstone and acid shales of Cumberland ridges. Its canopy iG2? G2

High-Elevation Red Oak Forest (Tall Herb Type) 1 This community includes forest vegetation, with a closed to very open canopy, where <i>Quercus rubra</i> mG2 G2

Southern Blue Ridge Heath Bald Oak Woodland1 This association consists of open woodlands dominated by stunted red oaks, over a dense layer of ericaceouG2 G2

Shumard Oak - Chinkapin Oak Mesic Limestone Forest 2 This deciduous forest association accommodates mesic forests dominated by <i>Quercus shumardii</i> and G2G3 G2

Southeastern Highland Rim Post Oak - Blackjack Oak W 2 These woodlands dominated by <i>Quercus stellata</i> and <i>Quercus coccinea</i> occur in the southeasoodland G2G3 G2 

Piedmont Acidic Hardpan Woodland 2 This association occurs on acidic clay pans in flat terrain of the Piedmont. The canopy is closed to fairly open G2 G2

Piedmont Montmorillonite Woodland 2 This community occurs most commonly on mafic igneous rocks found in the Triassic basins in the Piedmont G2G3 G2

Piedmont Basic Hardpan Forest (Rocky Type)2 Piedmont woodlands of dry, upland, montmorillonitic clay soils derived from mafic volcanic rocks. The canopG2 G2

West Gulf Coastal Plain Post Oak - Loblolly Flatwoods 2 This association is found in the West and Upper West Gulf Coastal Plain ecoregions of eastern Texas and pG2G3 G2

Post Oak Interior Highlands Scrub Woodland 2 This association consists of stunted (1.5-4 m tall) oak woodlands occurring on summits of the higher elevatioG2 G2

Black Belt Post Oak Woodland 2 This Black Belt woodland has an open canopy dominated by <i>Quercus stellata, Quercus muehlenbergii</i>G2G3 G2

Post Oak Novaculite Woodland 2 This woodland is known from outcrops of novaculite (and other substrates) in the Ouachita Mountains of OklG2 G2

Nashville Basin Post Oak Woodland 2 This woodland is restricted to the Inner Nashville Basin of Tennessee, where it occurs in association with LimG2? G2

Western Highland Rim Post Oak Barrens 2 These woodlands are dominated by <i>Quercus stellata</i>; a scattered to dense subcanopy of <i>JuniperuG2G3 G2 

Texas Gulf Coast Live Oak - Sugarberry Forest1 This association includes woodlands occurring along the upper Gulf Coast of Texas north of Galveston Bay oG2G3 G2

Gulf Coast Shell Midden Woodland 2 These are supratidal communities occurring on shell middens of Gulf Coast maritime areas; they receive stoG2G3 G2

Maritime Live Oak Hammock 2 This forest of barrier islands and related habitats has a low to moderately high tree canopy, often stunted and G2 G2

Live Oak - Pecan Woodland 1 This woodland of the upper Coastal Prairie region of Texas occurs within a matrix of coastal grassland. It is cG2 G2

Coastal Louisiana Chenier Forest 2 This association includes forests of cheniers (old isolated beach ridges surrounded by marsh) of coastal LouG2 G2

Florida Panhandle Maritime Live Oak Hammock2 These maritime hammocks occur in small parcels along the shoreline of the northern Gulf of Mexico in westeG2Q G2

Atlantic Coastal Fringe Evergreen Forest 1 These generally closed forests of the mainland coastal fringe of the Atlantic Coast have diverse canopies anG2 G2

Atlantic Coast Maritime Evergreen Forest 1 This community is a low- to moderate-stature, broad-leaved evergreen forest that is often, though not alwaysG2 G2

2 This forest occurs in the outer Coastal Plain of Louisiana, on natural levees and terraces of the former channG2G3 G2

Water Oak - Live Oak Forest 2 This bottomland hardwood forest occurs along small rivers and streams within the historic coastal prairie maG2G3 G2 

2 This forest occurs in the outer Coastal Plain of Louisiana, on extensive flats, closely associated with the more G2G3 G2 

Upper Texas Coast Live Oak Forest 2 This forest occurs along small rivers and streams within the historic coastal prairie matrix, now mostly in agriG2G3 G2 

Xeric Live Oak Hammock 2 This association represents one of two inland (not immediately adjacent to the coastline) hammocks or oak dG2G3 G2

1 Mangrove forests in island interior depressions, with significant understory development, in the Florida Keys G2G3 G2
1 This is a non-tidal, seasonally flooded mangrove community, occurring over deep organic soils containing m

G2? G2

Subtropical Texas Palmetto Woodland 2 This community is a subtropical, evergreen forest dominated by a mixture of subtropical and temperate riveriG2 G2

Cabbage Palmetto Woodland 2 This community consists of pure to mixed, open stands of <i>Sabal palmetto</i>, often with <i>Juniperus virgG2? G2

Temperate Hydric Hammock 2 This association represents temperate hydric hammocks of Florida and adjacent Georgia. Although this type G2G3 G2

Subtropical Hydric Hammock 2 This plant association comprises hydric hammocks of coastal peninsular Florida, with some tropical componG2? G2

South Florida Willow Thicket 2 This wetland community of the southern Florida Everglades region is a dense thicket dominated by <i>Salix G2? G2

Central Florida Willow Thicket 2 This seasonally flooded willow community occurs in peaty depressional wetlands. <i>Salix caroliniana</i> is G2G3 G2

Middle Atlantic Coastal Plain Carolina Willow Dune Swale 2 This association occupies swales in forest-dominated dune fields, with scattered <i>Salix caroliniana</i> and G2? G2

Chihuahuan Desert Willow Dune Depression 2 This association occupies interdune ponds in quartz sand dunes, with seasonal flooding. Following flooding sG2? G2

2 This deciduous riparian woodland has an open, 5- to 7-m canopy dominated by small-diameter <i>Salix goodG2 G2

Northern Gulf Tidal Pond-cypress Forest 2 This vegetation of floodplains is found near mouths of rivers just inland from coastal salt marshes in the East G2? G2

South Florida Cypress Strand 2 This association represents cypress strands of the south Florida Everglades region, where they are apparenG2? G2

South Florida Cypress Dome (Pond Apple Type) 2 Dome-shaped <i>Taxodium ascendens</i> communities, generally with abundant epiphytes. Traditionally seG2? G2

Atlantic Coastal Plain Pond-cypress Depression (Longleaf Three-awn Type) 2 This depression woodland is found in Carolina bays and swales in coastal South Carolina. <i>Taxodium asceG2G3 G2

South Florida Cypress Dome (Coco-plum Type)2 Characteristic species include <i>Magnolia virginiana, Annona glabra, Ilex cassine</i>. G2? G2

Coastal Plain Small Depression Swamp (Pocosin Shrub Type) 2 This association includes clay-based Carolina bays and other seasonally flooded depressions, dominated by G2 G2

Atlantic Coastal Plain Pond-cypress Savanna 2 This community type occurs in seasonally flooded depressional wetlands, especially in clay-based Carolina bG2G3 G2

2 Stands of this association (which is restricted to southern tropical and subtropical Florida) exhibit a stunted, sG2G3 G2

2 This southern tropical Florida association is characterized by a stunted, scattered canopy (1.7-6 m tall) of <i>G2G3 G2

Pond-cypress Savanna 2 This open-structured savanna or woodland encompasses very acid, species-poor communities in which <i>TG2? G2 

Apalachicola River Tidal Swamp Forest 2 This association represents one of several freshwater tidal swamp forest types found in the Florida portion of G2 G2

Bald-cypress - Swamp Blackgum Basin Swamp1 Stands of this forest are dominated by <i>Taxodium distichum, Nyssa biflora, Acer rubrum</i>, and <i>MagnG2G3 G2 

2 This association represents tidal rivermouth swamp forests of the northern Gulf of Mexico. This type is knowG2 G2

Bald-cypress - Swamp Blackgum Nonriverine Swamp Forest 2 This forest community is dominated by <i>Taxodium distichum</i> and <i>Nyssa biflora</i>, with less frequeG2G3 G2 

Edwards Plateau Bald Cypress - Sycamore Gallery Forest 2 This open forest is dominated by <i>Taxodium distichum</i> with <i>Platanus occidentalis</i> usually occurrG2 G2

2 These open forests dominated by <i>Taxodium distichum</i> and <i>Platanus occidentalis</i> occur along rG2Q G2

Bald-cypress / Shoreline Sedge Woodland 2 This community occurs in narrow bands along the fringes of wind-tidal marshes on the Northwest River and G2? G2

2 These are seasonally flooded tropical <i>Taxodium distichum</i> swamps, with a tropical/temperate understG2? G2

Mid-Atlantic Tidal Freshwater Cypress Marsh 2 Stands of this association typically consist of large, scattered <i>Taxodium distichum</i> over a graminoid-dG2G3 G2

Alabama Red Hills Mesic Hardwood Bluff Forest 1 This community is found on mesic, north-facing bluffs in the Alabama Red Hills of the East Gulf Coastal Plain G2G3 G2

Southern Appalachian Cove Forest (Rich Foothills Type) 2 Forests of steep, protected coves and slopes at the lower elevations (below 610 m [2000 feet]) of the southeG2G3 G2

Swamp Forest-Bog Complex (Typic Type) 2 This palustrine forest has a closed or open canopy and an open to dense shrub layer, interspersed with smaG2 G2

High-Elevation Hemlock - Yellow Birch Seepage Swamp 2 This community is currently known from scattered sites in the northern Blue Ridge and Ridge and Valley provG2 G2 

Southern Appalachian Acidic Cove Forest (Silverbell Type) 1 This association includes forests dominated by <i>Tsuga canadensis</i> and <i>Halesia tetraptera var. monG2 G2

Carolina Hemlock Forest (Pine Type) 2 This association is known from shallow soils over sedimentary and metasedimentary rock strata on exposed G2 G2

Carolina Hemlock Forest (Typic Type) 2 These forests occur with canopies dominated by <i>Tsuga caroliniana</i>, without admixtures of <i>Pinus</G2 G2

Sugarberry - Cedar Elm Calcareous Floodplain Forest 2 This community occurs on older, low-gradient river floodplains primarily in the Gulf Coast Prairies and MarshG2G3 G2

2 This giant conifer forest community occurs in the Cascades of southern Oregon where it thrives on flat or conG2G3 G2

1 This giant coniferous forest association is codominated by <i>Abies concolor, Chamaecyparis lawsoniana</iG2 G2

1 This giant coniferous forest association occurs in narrow draws and streamsides in southwestern Oregon anG2 G2

2 This highly variable coniferous forest association is found in southwestern Oregon and northwestern CalifornG2 G2

2 This association is a rare, mixed-conifer community located on cool, wet sites and codominated by the regionG2 G2

2 This association has been described only from southwestern Oregon, on the Illinois Valley and Applegate DiG2 G2

2 This evergreen forest association is a rich, mixed conifer-deciduous forest occurring on active floodplains anG2 G2 

2 This association is only known from the Warner Mountains of south-central Oregon and northeastern CaliforG2 G2

2 The association is found in south-central Oregon and possibly northeastern California, in mountains between G2 G2

2 This minor forest association has been described from the southern Rocky Mountains in northern Colorado aG2? G2

2 This high-elevation forest is codominated by <i>Abies concolor</i> and <i>Pseudotsuga menziesii</i> with inG2 G2

1 This is a montane forested riparian association found in higher elevation drainages along the Mogollon Rim aG2G3 G2

2 This mixed-conifer forest occurs locally on Mount Hood National Forest in Oregon and in California. Stands oG2 G2

2 This is a conifer forest association with a rich forb undergrowth. It is located near stream bottoms in the easteG2 G2

1 This herb-rich coniferous forest association is found on the eastern slope of the Oregon Cascades. Stands aG2 G2
2 Giant <i>Pseudotsuga menziesii</i> old-growth trees dominate the overstory of these closed-canopy, valley 

G2 G2

1 This is an evergreen conifer woodland association generally found on ridgetops and rocky sites in the easterG2G3 G2

1 This plant association is known from stands located between the South Fork of the Clearwater and Salmon rG2 G2 

2 This is an evergreen conifer forest association restricted to the eastern Cascades near the Columbia River gG2G3 G2

1 This forest association occurs within the maritime-influenced climatic region of the northern Rocky Mountains G2 G2

1 This is an evergreen conifer forest composed of two distinct tree canopies found mostly in the north-central RG2 G2 

1 This plant association is described for the western Idaho Batholith and eastern Blue Mountains ecoregional sG2 G2 

1 Endemic to southeastern Cascade Mountains of Washington, this association is found at higher elevations in G2G3 G2 

2 This association occurs only in the northeastern Olympic Mountains of W G2 ashington. Sites occupied are dry, uG2

2 This high-elevation forest is codominated by <i>Abies lasiocarpa</i> and <i>Picea engelmannii</i> with occaG2 G2

2 This association primarily occurs in the Puget Lowlands of Washington, the northern end of the W G2G3 G2 illamette V

2 This western Colorado riparian forest occurs on broad alluvial floodplains with strongly meandering stream cG2 G2

2 This plant association occurs in the Overthrust Mountains of northeastern Utah, in northwestern Colorado anG2? G2 

2 G2? G2

2 This plant association is described from the Snake River canyon in western Idaho from sites at 460 to 800 m G2? G2

1 This minor woodland association is described from deep canyon bottoms of the Snake and Salmon rivers in G2G3 G2 

1 This woodland association is found in eastern Oregon and Idaho. Mean annual precipitation is 56 cm, which G2 G2

2 This association is described for the western portion of the Northwest Basin and Range, and the Owyhee UpG2 G2

1 This conifer forest association occurs very locally in southwestern Oregon and northern California. These forG2 G2

Port Orford-cedar Ultramafic Meadows 1 This is an open-canopy, coniferous forest found on metamorphic substrates, primarily serpentine and gneissG2 G2

2 This forest association is found on slopes and in drainages. Sites tend to be cool and moist with northern or eG2 G2

2 The distribution of this woodland association includes localized occurrences in southern and southeastern ArG2G3 G2

2 Stands of the <i>Cupressus macnabiana</i> forest occur from 300-800 m elevation in northwestern CalifornG2 G2

2 Stands of this community typically occur on lower canyon slopes and in ravines from 200-900 m of elevationG2 G2

2 G2 G2

2 G2 G2

2 This mature riparian forest association is known only from the San Francisco River in southwestern New MexG2 G2

2 These are open woodlands or juniper savannas which are restricted to barren, ashy soils in the central OregG2 G2

1 This association is found on well-drained and moderately deep soils, of gravelly loam over basalt. This assocG2 G2

2 This is a low, shrubby woodland type growing on shallow, rocky soils on hogbacks, ridges and colluvial slopeG2G3 G2 

1 This woodland community is widespread north of the Mogollon Rim, in Arizona and adjacent mountains of NeG2 G2

2 This <i>Juniperus scopulorum</i>-dominated open woodland has been described from dry rocky ridges and G2? G2

1 This <i>Juniperus scopulorum</i>-dominated open woodland has been described from dry rocky ridges and G2 G2 

2 This woodland association has only been reported from north-central Colorado in Rocky Mountain National PG2 G2

2 This plant association is a `scarp woodland' known from shallow, rocky, calcareous, generally north-facing slG2 G2 

2 This association has been described from only the northern Rocky Mountains of Montana and their continuatG2G3 G2

1 This is a deciduous conifer woodland located above the limits of other conifers. It is found in the high elevatioG2G3 G2 

2 G2 G2

2 This association is most prevalent in the Challis Volcanics and Beaverhead Mountains Sections of east-centG2Q G2 

2 This association occurs in low-elevation valleys, from 760 to 915 m (2500-3000 feet), west of the ContinentaG2 G2

1 This association is restricted to the higher elevations of the Sacramento Mountains of New Mexico and the CG2 G2

1 This minor coniferous forest association occurs in the mountains of central and eastern Idaho, western W G2 G2 yom

1 These mixed conifer forests have been described from the White Mountains and Blue Mountains of east-cenG2 G2

2 This association is known only from the Front Range of north-central Colorado. It occurs from 3300-3450 m (G2? G2

1 This blue spruce association is known from Colorado, southern Utah possibly northern New Mexico. It is a coG2 G2

2 G2G3 G2

2 This association occurs along rivers and streams of the west-central and southwestern slope of the Rocky MG2 G2

2 This association occurs along the Pacific coast from northern California to British Columbia. It is a wetland tyG2G3 G2 

2 This mid-seral to climax association occurs on floodplains of rivers and creeks near the Pacific Ocean, from G2 G2 

2 This plant association is found primarily on peatlands occurring on distal outwash, uplifted tidal flats, and moG2G3 G2

1 This central and northern Rocky Mountain woodland association occurs in northwestern W G2G3 G2 yoming, western M

2 This subalpine woodland is found in Oregon's southeastern Cascades at elevations of 2135-2750 m (7000-9G2 G2
2 This is a conifer woodland found in the high elevations of the northeastern Cascades of W G2 G2 ashington extendin

2 This association is known only from the southern Arapaho National Forest in north-central Colorado, in the FG2 G2

2 This association is an open, valley bottom or low elevation woodland found on serpentine soils in southwesteG2 G2

2 G2 G2

1 This early to mid-seral association occurs sporadically along the coast between northern California and southG2 G2 

Madrean Woodland 2 This Madrean conifer woodland occurs in the 'Borderlands' of southeastern Arizona, southwestern New MexG2 G2

2 This Madrean conifer woodland occurs the Animas, Peloncillo, Chiricahua and Santa Catalina mountains in tG2 G2

Madrean Conifer Woodland 2 This Madrean conifer woodland occurs in the 'Borderlands' in southeastern Arizona and extreme southwesteG2 G2

2 This woodland association is known from western and south-central Colorado and eastern Utah. Stands occG2? G2

2 This woodland association occurs locally in the landscape in central and northern New Mexico, where it occuG2 G2 

2 This association occurs on moderate slopes of predominantly southeastern aspects at elevations from 1830 G2 G2

1 This Madrean conifer woodland occurs in the mountains of southeastern Arizona, southwestern New Mexico G2 G2

2 These woodlands are restricted to a very narrow area of serpentine habitat in southwestern Oregon and nortG2 G2

2 G2 G2

1 This is a high-elevation Ponderosa pine association, found between 1680 and 2105 m (5500-6900 feet). It ocG2G3 G2

1 Steep, rocky slopes near ridgetops that receive intense solar radiation are typical sites for this association. AG2 G2 

1 Known only from a limited area in the eastern Cascades of Washington, this association is restricted climaticG2G3 G2

2 This mixed evergreen-deciduous woodland occupies hot, dry sites between 645-1060 m elevation on the easG2 G2

2 This is a mixed conifer - deciduous broad-leaved woodland association confined to the eastern Cascades fooG2G3 G2

2 This association is an open woodland typified by large fire-resistant trees, found on the eastern edge of the CG2G3 G2 

2 This woodland occurs in the western Black Hills of South Dakota and in the Powder River Basin and Little MG2Q G2 

2 This coniferous riparian woodland is found along foothill and lower montane canyon bottoms of the southern G2 G2

2 This woodland is a minor association occurring on cool slopes in the foothills of the Bear's Paw Mountains. SG2 G2

2 This coniferous forest of the Siskiyou Mountains typically grows on south- to southeast-facing slopes betweeG2Q G2 

2 This type is thought to be restricted to isolated ridges in the Blue, Ochoco and W G2G3Q G2 allowa mountains in Oregon

1 This woodland is reported from the Fremont National Forest in Oregon. Elevation ranges from 1770 to 2135 G2G3 G2

2 This association has only been described from central and northeastern Oregon, and adjacent W G2Q G2 ashington a

2 Topography ranges from undulating to steep slopes ranging from 2-20% with slope position from low to bottoG2 G2

2 This semi-riparian forest is found on terraces along perennial streams and large washes. The upper canopy G2 G2

1 This plant association is known from stands within the Idaho Batholith, Bitterroot Mountains, and Palouse PraG2 G2

2 This is an open woodland found on pumice or ash in the East Cascades and Modoc Plateau in southern OreG2 G2 

2 This forest is endemic to the eastern Cascades of central Oregon. It is found on a narrow elevational belt betG2 G2

1 This woodland is found in the southern Blue Mountains, the Ochoco Range, and southeastern Oregon CascaG2G3 G2

2 This is an open woodland found in the eastern Cascades ecoregion in south-central Oregon. This associatioG2Q G2 

1 This is a lowland forested riparian association known from the Gila River watershed in New Mexico and poteG2 G2

2 This riparian forest is found along perennial and seasonally intermittent streams in the foothills zone of isolatG2 G2

2 This riparian woodland association is known from southwestern New Mexico, but it likely occurs in southeastG2G3 G2

1 This semi-riparian woodland association occurs in north-central WG2G3yoming, western Colorado and northern NG2

2 This plant association occurs on gently to moderately sloping stream terraces at elevations between 1500 anG2G3 G2

2 This is a riparian woodland of low-elevation (1600-2500 m [5240-8200 feet]) foothills in Colorado, New MexicG2Q G2 

2 This deciduous riparian forest occurs on stream terraces and adjacent floodplains in the LaSal and Abajo moG2G3 G2 

2 This riparian plant association is a lush deciduous forest occurring on an active alluvial floodplain of Sand CrG2? G2

1 This association is known from the Blue Mountains of eastern Oregon, through the Columbia Basin to the CaG2 G2 

2 This association has been described from the foothills of the eastern slope of the Rocky Mountains in northwG2 G2 

2 This association occurs on well-developed floodplains of lowland rivers in western Oregon, western W G2G3 G2 ashing

2 G2Q G2

1 This association is apparently limited to the western Olympic Peninsula, W G2G3 ashington, where it occurs in valleG2 

2 This minor streambank forest occurs in narrow, very steep valleys along perennial and ephemeral streams bG2 G2 

1 This mature riparian forest association is found in the middle Pecos and Rio Grande basins of New Mexico aG2G3 G2

2 This mature riparian forest association is found in the San Juan River drainage in northwestern New Mexico G2G3 G2

Cottonwood / Saltgrass Floodplain Woodland 2 This riparian woodland association is described from major river systems of eastern Colorado, primarily the SG2 G2 

1 This mature riparian forest association is found in the San Juan and Rio Grande watersheds in northern and G2 G2
1 This mature riparian forest association is found in the middle Rio Grande basin in north-central New Mexico a

G2G3 G2

1 This woodland plant association occurs sporadically on clayey soils along broad, braided channels in low-lyinG2 G2 

2 This association is found in the Great Plains of central and eastern Montana, southern Alberta, southern SasG2G3 G2

2 This association is found in the Canadian River and Pecos basins in northeastern New Mexico, probably elseG2G3 G2

2 This association is found in the Rio Grande basin in central New Mexico. This mature forest association is foG2 G2

2 The type is known only from gypsum dunelands of the Tularosa Basin in south-central New Mexico at elevatG2G3 G2 

2 This woodland association is documented from the Colorado, Yampa and San Miguel/Dolores river basins in G2 G2

2 This lower-montane riparian association is known from small tributaries of the Rio Grande in northern New MG2G3 G2

2 This type is known only from interdune swales of gypsum dunelands of the Tularosa Basin in south-central NG2G3 G2

2 This is a lowland forested riparian association known from central and southeastern Arizona, southwestern NG2G3 G2

2 This is a lowland forested riparian association known from the Gila River watershed in New Mexico and has G2 G2

1 This is a lowland forested riparian association known from the Gila River watershed in New Mexico and poteG2 G2

2 This community type occurs in lowland river valleys of the southwestern watersheds of the Gila River Basin oG2 G2

2 This community occurs as small isolated stands or as linear bands that parallel stream channels in the TransG2 G2

2 This forested riparian association is known from canyon bottoms in southwestern New Mexico and southern G2Q G2

2 This lowland riparian woodland is described from central and southern coastal interior ranges of California, sG2 G2

1 This open riparian woodland is found generally along small, perennial and seasonally intermittent streams in G2 G2

2 This forest type has been described from the southern parts of the W G2 yoming and Salt River mountain ranges G2 

2 This mixed deciduous-and-evergreen woodland occurs on mountain slopes from western W G2G3 G2 yoming south to 

2 This deciduous forest occurs on primarily on northerly and easterly exposures but has been seen on southeaG2G3 G2 

2 According to Christy (2004), the single known occurrence of this association in Oregon is in a seasonally flooG2 G2 

1 This association is a wide-ranging, linear or small-patch community type, found in eastern W G2 G2 ashington and O

2 This association occurs on the slopes of ridges and mountains in northwestern W G2 G2 yoming and western Colora

2 Stands of this localized forest type are found in moist depressions at high elevations in western W G2? G2 yoming. S

2 This minor riparian forest association is found east of the Continental Divide in a mountainous region of soutG2 G2

1 This rare but widespread forest occurs on slopes at high elevations in the mountains of western W G2 G2 yoming, so

2 G2G3 G2

2 G2 G2

1 This is a seral, fire-dependant association, which did not cover an important part of the presettlement landscG2G3 G2 

1 This giant conifer forest is found near the northern distributional limit of <i>Sequoia sempervirens</i>. <i>SeqG2 G2

2 These giant conifer forests are found in the coastal fog zone of southwestern Oregon and northwestern CalifG2 G2

2 This association occurs at lower elevations in the rain shadow of coastal mountains where mean annual precG2 G2

1 This association occurs below 460 m (1500 feet) elevation in west-central portions of the Puget Lowland of W G2 G2 

2 This giant conifer forest association is found in a narrow band along the coast of central Oregon. It occurs prG2 G2 

1 This association occurs below about 300 m (1000 feet) elevation in central portions of the Puget Lowland of G2 G2 

2 This association has been reported from colluvial slopes, ridges, mountains and canyon walls in northwesterG2Q G2 

2 This association has only been described from the eastern portions of the Mount Hood National Forest in the G2 G2 

2 This association occurs from sea level to about 610 m (2000 feet) elevation in the Puget Lowland, W G2G3 G2 ashingto

2 G2? G2

2 This association occurs on rocky, steep to very steep (20-65 degrees), relatively dry, north- to northwest-faciG2G3 G2

2 <i>Pseudotsuga menziesii / Piptatherum micranthum</i> Woodland occurs in the Missouri River Breaks souG2Q G2

1 This minor conifer forest association occurs in mid-elevations of mountain ranges of southwestern New MexiG2 G2

2 This association occurs from sea level to about 1220 m (4000 feet) elevation in the northern portion of the PuG2G3 G2 

2 This forest association is known from the eastern side of the Cascades around Mount Hood and is reported fG2 G2

2 This Madrean semi-riparian woodland occurs in the "Borderlands" area of southwestern New Mexico and poG2 G2

1 This forest association occurs in the southern Puget Lowland of western W G2 ashington, the W G2 illamette Valley a

2 This a mixed woodland occurs in northern California and southwestern Oregon. Large stands of this communG2 G2 

1 G2 G2

2 This woodland association occurs in the Puget Lowland of western W G2 ashington and the Georgia Basin of soG2

2 G2 G2

2 This is a deciduous woodland association with a deciduous shrub undergrowth. It is generally associated witG2G3 G2 

1 Stands range from open woodlands to closed canopy forests dominated by <i>Quercus garryana</i>. <i>PseG2 G2
2 These woodlands are found in California's Coast Ranges, the Great Central Valley, the foothills of the Sierra 

G2? G2

2 This association is known only from the larger of the Channel Islands off the coast of southern California: SaG2? G2

2 According to Christy (2004), the habitat for this association is shrub swamp around shallow lakes and pondsG2 G2 

2 G2 G2

2 This association occurs on the western slope of the southern Cascade Mountains and northern Klamath MouG2 G2

1 This association is characteristically found on primarily eastern aspects, on the upper to middle third of the sG2G3 G2 

1 This association is described based on data collected on 30 plots located in northern Idaho in the Clearwater G2? G2 

1 This is a late-seral evergreen conifer forest found in the mid elevations in the Okanogan Highlands east of thG2 G2 

2 This evergreen forest association is found on the west slope of the Oregon Cascades, on the east slope of thG2 G2 

1 This plant association occurs within the Pacific maritime-influenced climatic regions of the northern Rocky MoG2 G2

1 This regionally endemic plant association is described as a unit of potential natural vegetation from stands loG2 G2 

2 This mixed-conifer/hardwood association occurs locally in southern Oregon and possibly northern California. G2 G2

2 This is an old-growth evergreen conifer forest restricted to the Pend Oreille River drainage in northeastern W G2 G2 

1 This association has only been described from a small area of the Olympic Mountains, on some of the driest G2 G2 

1 This plant association is described from sites located primarily in the upper Clearwater River drainage, within G2 G2
GRank Review Date GRank Reasons Nations Subnations

6/2/2005 This floodplain community is uncommon within a limited range of coastal British Columbia, Canada. It has experienced intensive harvesting in thCA BC

9/19/2005 This coniferous floodplain forest is uncommon within its range and has been extensively harvested in the past. It has continued to decline in recCA BC

4/11/2006 This community type is sparsely distributed within a very small range (confirmed to occur only in southern coastal mainland and islands of BritisCA, US? BC, WA? 

4/11/2006 This forested wetland is extremely rare within its range (confirmed to occur only in southern British Columbia coastal mainland and islands and PCA, US BC, OR, WA 

4/11/2006 This forested plant community was not common within its range (southern British Columbia coast, San Juan Islands and Olympic Peninsula of W CA, US BC, WA 

9/20/2005 This coniferous floodplain forest is uncommon within its range and has been extensively harvested in the past. It has continued to decline in recCA BC

11/18/1997 This swamp forest community is confined to southern New Jersey, found only on Cape May. The habitat, stream headwaters of the Cape May gUS NJ

1/24/2005 This type appears to be endemic to a portion of the Potomac Gorge in Maryland and Virginia that is geomorphically unusual and has a near-uniqUS MD, VA

1/30/2007 This community is restricted to maritime bluffs and backdunes dominated by American beech. It is naturally restricted by available habitat on LoUS NY

11/10/1997 This is a small-patch type that is restricted in known distribution to seven patches (two occurrences) in a single high-elevation headwater basin iUS MD?, PA?, WV 

3/1/2002 US NJ, NY

11/20/1997 This community is limited to small seasonally flooded depressions of the coastal plain of Maryland and Virginia. The community is naturally smaUS DE, MD, VA

11/15/1997 This community is known only from West Virginia, where it is restricted to west-facing side ridges of Pine Knob in Pendleton County. There are fUS WV

12/8/1998 This community occurs in fewer than five locations rangewide, with total rangewide acreage of less than a few hundred acres. Additional occurreUS PA?, WV

5/21/2007 This vegetation is restricted to the Allegheny Front in W US est Virginia and to the Catskill Mountains of New York. The likelihood of the discovery of NY, WV 

12/9/1998 There are fewer than 6 occurrences of this type rangewide, and these are restricted to two pine barrens landscape complexes: the Long Pond BUS NY, PA

3/22/1999 US NJ

11/9/1998 This community is restricted to areas of impeded drainage within northern sandplains. Only one occurrence is currently documented, but there mUS NY

12/2/1998 This maritime woodland community is restricted to major coastal dune systems of the mid-Atlantic region. Only 10-20 occurrences are estimated US DE, MD, VA

11/18/1997 This maritime shrubland community is restricted to a narrow range on coastal dunes of barrier islands on the mid-Atlantic coast. It does not occuUS DE, MD, NJ, VA

1/25/2005 The type occurs in a limited geographic area and is restricted to special habitat conditions within high-gradient river stretches. The total known aUS DC, MD, WV?

2/15/2007 This community is restricted to dry, calcium-rich, shell-containing soils of the eastern Virginia and Maryland Coastal Plain. This community is naUS DC?, MD, VA

6/22/1998 There may be fewer than 20 occurrences in the Black Hills, its only known location. US SD, WY

6/22/1998 There are probably fewer than 60 occurrences rangewide. Occurrences tend to be small, averaging less than 20 acres, so there is probably less CA, US IN, MI, NY, OH, ON, PA, VT

2/27/2000 There are probably fewer than 20 occurrences in Kansas, the only state from which this community is reported. Currently there are 557 acres doUS KS

6/22/1998 There are probably fewer than 20 high quality occurrences for a type that has a relatively restricted range. Only one occurrence, a 10 acre tract US IA, IL, MO

6/22/1998 No sizeable examples of an intact rich soil savanna or woodland are known to exist in Illinois or W US IL, MO, WI isconsin. Most have been destroyed or conve

6/22/1998 There are probably fewer than 20 occurrences of this community rangewide. This type has a somewhat restricted distribution in a predominantly US KS, NE, OK?

10/24/2002 This community type has a very restricted distribution on the northern and eastern flanks of the Black Hills. Surveys of this type have been restrUS SD, WY

6/22/1998 This is an unusual community. Few examples remain because the soils usually support forests and succession has extirpated many examples oUS IL, KY?, MO?

12/11/1998 This association occurs as scattered wetland inclusions in a predominantly upland flatwoods environment, which in most parts of its range are sUS AL?, LA, MS, TX

1/4/2000 This community has a naturally restricted distribution, occurring only on the highest elevation peaks of the southern Appalachian Mountains. It eUS NC, TN 

7/15/1994 This community occurs as island-like stands in the southern Appalachian Mountains. It has a naturally restricted distribution and exists in only a US NC, TN, VA 

1/31/2001 The complete range of this association is not known. It is presumably restricted to calcareous bluffs of the Upper East Gulf Coastal Plain, this beUS AL, LA?, MS

12/14/1998 As currently delimited, this relictual hardwood-dominated forest is restricted to a few mesic limestone canyon systems in Bell and Coryell countieUS TX

10/15/1996 US? TX?

1/31/2001 This floodplain depression forest occurs at very few sites in the floodplains of rivers in the Blue Ridge physiographic province. It is naturally very US NC, TN?

1/10/1998 At the turn of the century, a monospecific stand of pond-apple (<i>Annona glabra</i>), some 3 miles wide, was found along the southern border US FL

10/15/1996 MX?, US TX

1/10/1998 This community is of restricted extent and range and is threatened by exotic species. US FL

1/23/2000 This community is known definitely from a single site of about 10 square kilometers in Pender County, North Carolina. It is possible that this comUS NC

1/10/1998 Estimated extent in United States is about 120 hectares (300 acres). This community has been reduced by coastal development in the Florida KUS FL

1/31/2001 This community type is apparently very rare, and restricted to calcareous soils or shell hash in the maritime situations on the south Atlantic CoasUS NC, SC

12/11/1998 This association is restricted to the Lower Rio Grande Valley of southern Texas and adjacent Mexico, containing subtropical elements not found MX, US MXTM, TX 

9/13/1997 US FL

9/13/1997 US FL

9/13/1997 US FL

1/23/2000 This community type appears to occur only at Buxton W US oods, Dare County, North Carolina, where it occurs as a recurring community in a series NC

10/2/1998 This community is known from a few sites in the lower Rio Grande valley of Texas, in Cameron and Hidalgo counties, and apparently ranged (at MX, US MXTM, TX

9/14/2006 This type is distributed at low frequency from Alabama to Georgia and Florida in the East Gulf Coastal Plain. It is not abundant anywhere. This cUS AL, FL, GA, MS

12/28/2000 This community is restricted to the western Florida parishes of eastern Louisiana and areas of adjacent southwestern Mississippi. It is thought to US LA, MS
11/1/2002 This community has a very restricted range with scattered occurrences of small acreage. Many occurrences have been, and continue to be, sev

US GA?, NC, TN, VA? 

11/1/2002 This community has a very restricted range with scattered occurrences of small acreage. Many occurrences have been, and continue to be, sevUS NC, TN, VA? 

1/10/1998 This community was naturally rare, but has also been greatly reduced in extent by urban development, with a estimated remaining extent of 985 US FL

10/23/2002 This community was naturally rare, but has also been reduced in extent by urban development, with an estimated remaining extent of 1485 hectUS FL

10/20/1996 This community is probably very rare. US NC, VA

12/14/1998 This community type is nearly historic; there are no known examples remaining in natural condition. It was formerly a widespread type in the BluUS KY

12/18/2000 This community is restricted to deep-soil, calcium-rich, habitats in the Bluegrass Basin of Kentucky, the Nashville Basin of Tennessee, and possUS KY

1/23/2000 This distinctive community is documented only from a few locations in estuarine areas of eastern North Carolina. Known occurrences are up to 4US NC

1/23/2000 This community appears to be endemic to saturated, peaty soils subject to periodic and seasonal flooding, associated with rare natural lakes in US NC

2/11/2004 At present this community is known only from a single site in eastern Texas, and few additional sites are likely. The natural range of this type is US LA?, TX 

1/10/1998 This community is restricted to the Everglades of southern Florida. It is affected by altered hydrology and fire regimes. US FL

12/1/1997 US FL

1/30/2001 This association is limited to exposures of Pleistocene Limestone (oolite) of the Miami Formation in the Florida Keys. The only definite occurrenUS FL 

6/20/1997 There are probably fewer than 20 occurrences rangewide. Currently 4 occurrences have been documented from Missouri (where it is ranked S2US AR?, MO, TN 

11/30/1999 Though this community occurs in natural drainages, its hydrology is not fully understood because the hydrology of the one known occurrence haUS LA, MS?

1/17/2001 This community type is very limited in potential occurrence. It occurs only in isolated upland depression ponds in the Piedmont, which are very rUS NC

5/23/2005 This community type is very limited in potential occurrence. It occurs only in isolated upland depression ponds in the Ridge and Valley (and possUS AL, GA, TN?

11/26/2007 Known only from two protected sites on North Carolina's Outer Banks (Mid-Atlantic Coastal Plain), this wetland forest is extremely rare and vulnUS NC, SC

2/23/1999 This community has a naturally restricted distribution and has been subject to major acreage reduction during the early part of the 20th century aUS NC, TN 

4/30/1998 The community is geographically and environmentally restricted to the highest elevations of the Southern Blue Ridge. Very few occurrences are US NC?, TN, VA?

12/31/1997 This community has a highly restricted range, occurring only within the spruce-fir zone of the southern Appalachians. It is restricted to steep perUS NC, TN?, VA?

1/10/1998 This community is restricted to near-coastal areas in the Florida Panhandle. Few occurrences are known. US FL

11/9/1997 This sand pine woodland association is restricted to a particular soil type and topographic situation along the coast of peninsular Florida. It is onUS FL

6/23/1997 This sand pine woodland association is restricted to a narrow band of the outer Gulf Coastal Plain of Panhandle Florida. W US FL ithin this very limited 

12/31/1997 This sand pine woodland association is restricted to a particular soil type and topographic situation in the southern portion of the Lake W US FL ales Rid

6/15/2004 As currently understood, this community is confined to the Upper East Gulf Coastal Plain of Mississippi. No rangewide inventories have been coUS AL, FL?, GA?, MS, TN? 

5/15/2002 There are probably fewer than 20 high-quality occurrences of this community throughout its natural range; it is reported from western Louisiana US LA, TX 

10/22/2002 This community is associated with exposures of fractured mafic metavolcanics of the Carolina Slate Belt, a rare edaphic situation. It is apparentlUS NC

10/23/2002 These open <i>Pinus echinata</i> woodlands were more common historically. Currently few mature, high-quality examples of this community exUS AR, MO, OK

1/10/1998 This community is endemic to southern Florida, occurring in the lower portion of the Florida Keys and ranging from the National Key Deer RefugUS FL 

1/10/1998 This community is restricted to the southwestern tropical tip of the Florida peninsula. Though highly restricted in distribution and extent, the comUS FL

1/10/1998 This community occurs in Dade County, Florida, ranging from Biscayne Bay, south through the Long Pine Key area of Everglades National ParkUS FL

12/2/1999 Known occurrences of this community are restricted to fire-sheltered, poorly drained flatwoods of the coastal plain of the southwestern portion oUS LA

10/10/1997 This saturated longleaf pine woodland association is apparently restricted in distribution to southern Mississippi. This community is apparently nUS LA?, MS

1/31/2001 This woodland is maintained by fire. Attempts should be made to reconstruct a more natural fire frequency and periodicity. This community is raUS SC 

12/4/1999 This association only occurs west of the Mississippi River in west-central Louisiana and possibly eastern Texas. It is naturally restricted to extreUS LA, TX 

4/19/2004 This longleaf pine association is apparently restricted to an area of approximately 70 square km centered on Jameston, South Carolina, on the nUS SC 

2/17/2004 This association is apparently endemic to Georgia where it is known from only one location at Burks Mountain, Columbia County. This site is onUS GA

10/10/1997 This saturated longleaf pine - slash pine woodland association is found only in a restricted range and under a specific set of habitat conditions. IUS FL, GA, SC?

10/10/1997 This saturated longleaf pine - slash pine woodland community occurs in pineland swales and is restricted in distribution to the Atlantic Coastal PUS GA, SC

10/10/1997 This saturated longleaf pine - pond pine woodland association is naturally rare, restricted both in range and in the substrate on which it occurs. IUS GA, NC, SC

12/31/1997 This saturated longleaf pine - pond pine woodland association is restricted both in range and in the substrate on which it occurs, being found onUS SC

12/31/1997 This saturated longleaf pine - pond pine woodland association is restricted both in range and in the substrate on which it occurs. It is naturally raUS NC

12/31/1997 This saturated longleaf pine - pond pine woodland association is restricted both in range and in the substrate on which it occurs. It is only found US NC

12/31/1997 This saturated longleaf pine - pond pine woodland association is restricted both in range and in the substrate on which it occurs. It is only found US NC

12/31/1997 This saturated longleaf pine community is restricted in distribution to the lower Piedmont of North Carolina (Moore, Montgomery, and Anson couUS NC, SC?

12/31/1997 This longleaf pine - loblolly pine - pond pine woodland occupies wet-mesic savannas on loamy soils in the middle Coastal Plain of southeastern US NC, SC?

10/16/1997 This saturated longleaf pine woodland association is restricted to South Carolina. It is naturally rare and limited to small occurrences. It is part of US SC

12/31/1997 This saturated longleaf pine woodland association is restricted to South Carolina. A naturally rare and restricted community type, this longleaf piUS SC

12/20/1999 This association is part of the endangered Longleaf Pine Ecosystem that was once dominant in the southeastern coastal plain and which has suUS AL, FL, GA 

2/4/1999 This longleaf pine woodland association is found in a restricted range and specific set of habitat conditions and is susceptible to forest conversioUS LA, TX 

1/22/1998 This longleaf pine woodland association represents a type of sandhill scrub and is restricted to xeric sandy sites in the East Gulf Coastal Plain. RUS LA, MS?
10/10/1997 This xeric longleaf pine sandhill woodland association is found in a restricted range and specific set of habitat conditions. It occurs only on xeric 

US FL, GA

1/19/1999 This woodland community is restricted to the range of longleaf pine north of the distribution of <i>Aristida stricta</i>. It is only found in northeastUS NC, VA

12/14/1998 This community is limited to areas of sandstone outcropping in the sandhills of South Carolina. It is very limited in extent, occurring in a matrix oUS SC

1/31/2002 This peculiar <i>Pinus palustris</i> woodland community has a very restricted distribution, known only from a few sites associated with outcroppUS LA, TX 

12/31/1997 This longleaf pine woodland is an extremely rare community with a restricted distribution, being known only from northern Rapides Parish of the US LA, TX? 

4/20/2004 This association is restricted to wet Ultisols of the Atlantic Coastal Plain of South Carolina, particularly the wiregrass gap region, where it is natuUS SC 

12/31/1997 This saturated wetland longleaf pine association is restricted to the W US LA, TX? est Gulf Coastal Plain. It only occurs on rare saline soil types of the Pleisto

12/31/1997 This mesic longleaf pine woodland is found in a restricted range and specific set of habitat conditions. It is restricted to relict terraces along deepUS NC

10/22/2002 This community occurs on shallow, rocky soils associated with outcrops of serpentinized olivine in the Southern Blue Ridge. It is a unique commUS NC, TN

1/23/2000 This community type is documented only from The Glades, Grayson County, Virginia. It is restricted to an unusual edaphic situation, outcrops oUS TN, VA

12/31/1997 This saturated pond pine woodland association is found in a restricted range and specific set of habitat conditions. It occurs only in large peat doUS NC, SC?, VA

10/22/2002 This serpentine woodland is described from a small number of sites at low elevations in the Southern Blue Ridge of Georgia and North CarolinaUS GA, NC

12/4/2003 As currently understood and documented, this forest type is restricted to loess soils of Crowley's Ridge, Arkansas, a very limited natural range. US AR, MO?

1/30/2001 This community is currently restricted to Fort Pickett, Virginia, so far as is currently known, where it is maintained by frequent fires set by military US VA

12/4/2003 As currently understood and documented, this forest type is restricted to loess soils of Crowley's Ridge, Arkansas, a very limited natural range. US AR, MO?, MS?, TN?

3/26/2003 This community is currently restricted to Fort Pickett, Virginia, and Cowpens National Battlefield in upstate South Carolina, where it is maintaineUS NC?, SC, VA

12/15/1994 This community occurs over sandstone on dry ridges and south-facing slopes in the highest portions of the Ouachita Mountains. This communitUS AR, OK 

12/31/1997 This community has a very restricted range and only a few small occurrences are known to exist. It is associated with serpentine, dunite and peUS NC

12/20/1999 This high-fertility wetland forest is restricted to the Bluegrass Basin of Kentucky as defined. It needs to be closely compared with related MidwesUS KY

6/10/2008 EO Rank Estimator v.6.03 was used to assess the global rank. This community is known from only five sites (two of them very small) in extreme US NC, VA 

9/13/1997 US FL

10/11/2000 The global rank reflects that this community, as defined, is likely endemic to Coffee County, Tennessee. This is near the edge of the range of thUS TN 

12/14/1998 This rare association is restricted to the Ketona Formation in Bibb County, Alabama, where it occurs in association with rare dolomite glades, whUS AL

12/31/1997 The global rank reflects that this community is likely endemic to the southeastern Highland Rim of Tennessee (Coffee and adjoining counties). TUS TN

2/25/2004 This community is only known to occur in one location in the vicinity of Linville Caverns on the North Fork of the Catawba River. There are still nUS NC, SC?, VA?

1/2/2001 This mesic calcareous upland woodland community is restricted to areas of deep, moist soil usually on nearly level terrain or possibly in topograUS AR, LA?, OK?, TX? 

12/4/1999 As described, this forest association is naturally very restricted in range and environmental setting. It is only known from the Keiffer Prairie ReseUS LA, TX? 

12/2/1999 This deciduous forest association is naturally very restricted in range and environmental setting. It is only known from fire-protected mesic areas US AL?, LA, MS

12/3/1999 This deciduous forest association is naturally very restricted in range and environmental setting. It is only known from clayey calcareous substraUS LA 

12/2/1999 This deciduous forest association is naturally very restricted in range and environmental setting. It is only known from fire-protected small areas US LA

12/11/1998 This association occurs only in a very limited area of diabase geology in north-central North Carolina. This was a naturally very rare community, US NC

10/3/2002 This type is restricted to flats developed on montmorillonitic clay (shrink-swell) soils, derived from mafic igneous rocks (primarily diabase or gabbUS NC, SC

2/1/2001 This type has an extremely narrow geographic range (a single county in the W US TX est Gulf Coastal Plain) and is further confined to very rare ecologi

12/4/2003 US AR, MO?, MS?, TN?

1/31/2002 This association is naturally very restricted in range and environmental setting; it is only known from small areas of high pH soils associated with US AR, OK?, TX

12/8/1998 This community is very restricted in its area of occurrence, known only from a few salt domes in southern Louisiana and southern Texas. PotentUS LA, TX

6/10/2008 This maritime woodland is restricted to xeric dunes in extreme southeastern Virginia. Its limited habitat is threatened by coastal development. OUS VA

12/29/1998 This community type appears to be very rare and limited in distribution and occurrence. Some areas supporting this community were in row-crop US GA?, SC

12/29/1998 US GA?, SC

10/20/1996 US FL

10/20/1996 US FL

1/10/1998 This community is of very limited extent and is restricted to extreme southern Florida. US FL

9/13/1997 US FL

1/30/2003 All south Florida hardwood hammocks are rare and extremely geographically confined. As currently defined, this community is even more restricUS FL

1/10/1998 This is a very restricted tropical hardwood hammock type, and is restricted to estuarine shoreline situations. It has been reduced in extent, and hUS FL

12/14/1998 This association is related to a particular soil type, Bonsai Mucky Fine Sand; both the soil type and the association are apparently endemic to FrUS FL

1/31/2001 This pond-cypress community is limited to very rare maritime situations which have alkaline chemistry. Total known acreage of this community iUS AL, FL? 

6/26/2001 This community appears to be endemic to mineral soils on the edge of blackwater lakes in the exceedingly flat Tidewater region of northeastern US NC

10/4/2004 This association is limited to natural lake shorelines of the Outer Coastal Plain of North Carolina, a very limited habitat. The best known and proUS NC

12/31/1997 The rank of this association reflects its extremely limited habitat. The rank of this association reflects its extremely limited habitat. Fewer than fivUS VA

6/25/1997 US VA

1/10/1998 This community is extremely limited in range and extent, occurring in only a few small examples in the Florida Keys. It has been affected by coaUS FL
1/31/2001 This community type is limited to rare edaphic situations in the southern Appalachian Mountains of Virginia, Tennessee, and possibly Kentucky 

US KY?, TN, VA, WV? 

6/25/2001 The known geographic range of this community type is very limited, and occurrences are small and restricted to a narrow range of habitat conditUS VA

9/29/2004 This forest is restricted to steep gorges of the Alabama Cumberland Plateau, where the <i>Tsuga canadensis</i> represents a relictual disjunct US AL 

5/15/2002 <i>Tsuga caroliniana</i> communities, in general, have a restricted range, occurring only in the Southern Blue Ridge and upper Piedmont and aUS NC, TN 

12/14/1998 This riparian mesic blackland woodland community occurs in deep soils on relatively level terrain, typically as narrow communities bordering epUS AR 

11/30/1998 This is a rare association due to abiotic requirements. This association is infrequent throughout its range because it occurs on northern slopes wUS CA?, OR

10/21/1997 This is one of the rarest plant associations in Oregon. Always naturally restricted due to its limited occurrence in the coastal strip of southwesterUS OR

11/14/1997 This is a productive, valuable, mature forest plant association which is largely unprotected. Because of an unusual climate and the distribution oUS OR

10/17/2002 This association is a closed-canopy forest that occurs in restricted range in the east Cascades of W US WA ashington near Mount Adams. There may be 

11/13/1997 This plant association is very rare, known only from a 105 m elevational band, below the summit on the northern slopes of Mt. Lemmon in the SUS AZ

10/21/2002 This is a very rare, very local forest community. It is restricted to the northern Oregon Coast Range and is assumed extirpated from southwesterUS OR, WA? 

12/1/1997 US HI

12/1/1997 US HI

12/1/1997 US HI

12/1/1997 US HI

12/1/1997 US HI

11/14/1997 There are less than five known occurrences of this association; it has been documented from the eastern Colorado Plateau (Kittel and Lederer 1US CO, UT 

11/2/1997 This plant association is a regional endemic of the Snake and Salmon river canyonlands in Idaho, Oregon, and possibly W US ID, OR, WA? ashington. It is descr

11/14/1997 This regional endemic plant association is described from the deeply incised terrain of the Snake and Salmon river canyons of Idaho and OregoUS ID, OR

11/2/1997 This regionally endemic plant association is described from the low-elevation reaches and high canyonland tributaries of the Snake River in IdahUS CA?, ID, OR, WA

11/14/1997 This regional to narrow endemic plant association is described from the lower reaches of the Salmon River and associated canyonland tributarieUS ID, OR

11/2/1997 This regionally endemic plant association is described from low-elevation reaches of the Snake River and associated deeply incised canyonland US CA?, ID, OR

1/31/2007 This regionally endemic plant community occurs on sites that show a history of chronic mass-wastage, in the warmest region of the inland maritUS ID

10/16/2002 This is a riparian community that occurs in one drainage in one W US ID, OR, W ashington and one Oregon county and in another drainage in one county in IdA 

10/16/2002 This riparian community is found in only three drainages in one W US ID?, OR, W ashington county and one Oregon county. It occurs in a narrow climatic zone (A

10/17/2002 A narrow endemic association that is known only from tributary streams of the Snake River in Oregon and W US ID?, OR, WA ashington. This riparian association 

11/30/1998 This association is known only from a small region in central Idaho of unusual geologic substrates combined with relatively dry and cool climatic US ID

1/3/2001 This is one of the rarest, most endangered communities in Oregon. All sites have been either destroyed or impacted, with logging and developmUS CA?, OR

11/14/1997 A naturally very restricted range of distribution of <i>Chamaecyparis lawsoniana</i> and the presence of an introduced disease has caused signUS OR

11/14/1997 A naturally very restricted range of distribution of <i>Chamaecyparis lawsoniana</i> has been compounded by impacts from logging and introduUS OR

10/14/1997 A naturally very restricted range of distribution of <i>Chamaecyparis lawsoniana</i> has been compounded by impacts from logging and introduUS CA, OR

10/21/2002 This association occurs only on northeast slopes, on unique soils, fairly close to the ocean in northern California and extreme southwestern OreUS CA, OR

10/15/1997 This is one of the rarest and most threatened plant associations in Oregon. Always naturally restricted due to the unique confluence of the distribUS CA?, OR

12/1/1997 US HI

12/1/1997 US HI

12/1/1997 US HI

10/21/2002 There are 4 known occurrences of this association in Oregon and an estimated 4 in W US OR, WA ashington, thought to cover only 20-100 acres. This assoc

12/1/1997 US HI

12/1/1997 US HI

10/16/1997 This association occurs on coastal sand dunes between northern California and central Oregon. A well-drained sand substrate, improving moistUS CA, OR

12/1/2000 This plant association is ranked G1 because it is found only on low-elevation hill slopes adjacent to the Stikine River Delta, Alaska. W US AK indblown s

12/16/2000 This very rare woodland association is restricted to a fairly narrow zone along the Pacific coast. Specific habitat conditions required by this assoUS CA?, OR

1/30/2007 This association occurs on stabilized coastal sand dunes distributed discontinuously between northern California and southwestern W US CA, OR, WA ashington

11/30/1998 This association is restricted to a very small area, and continues to decline outside of one occurrence in a state park. There are only a few restriUS CA?, OR

11/14/1997 This community has a somewhat restricted natural range in portions of the Puget Lowland and Georgia Depression of W US WA ashington and British C

11/7/1997 This association is probably limited in its distribution to the "Borderlands" of southeastern Arizona and southwestern New Mexico, and very northMX?, US AZ?, MXCH?, NM

10/21/1997 This association is limited in its distribution to the "Borderlands" of southwestern New Mexico, and possibly southeastern Arizona and very northMX?, US AZ?, MXCH?, NM

10/21/1997 This association is limited in its distribution to the "Borderlands" of southwestern New Mexico, and possibly southeastern Arizona and the northeMX?, US AZ?, MXCH?, NM

11/10/1997 This narrowly endemic plant association occurs in a semi-arid climatic region, on recent, unweathered mafic volcanic flows of the Snake River PUS ID

11/30/1998 This association occurs across the Siskiyou Mountain in southwestern Oregon. This is a low-elevation, fire dependent plant association, which is US CA?, OR

10/17/2002 This association is a nearly extinct type that occupies bogs in a portion of the Puget Lowlands. There are very few occurrences and they are all US WA

11/30/1998 This is one of the rarest and most threatened communities in southwestern Oregon. Logging, cattle grazing, development and fire suppression hUS CA?, OR
3/29/1999 This is a very rare association (which is actively threatened by development) known from interior valleys in southwestern Oregon and northweste

US CA?, OR 

3/29/1999 This is a very rare, and unique community, known from only two sites, both on BLM land. The association is restricted to a narrow range of soils US OR 

10/1/1997 Three examples of this type are documented. The possible range of sites that can develop examples of the type are restricted to serpentine soilUS WA 

10/28/2002 US WA

10/9/1997 This community is restricted to a small area in northeastern W US ID, Washington and adjacent Idaho and to sandy or other coarse-textured soils. Known A

2/1/1996 This association is known from only one location of 245 hectares in central Oregon on an unusual substrate. However, it is reported to exist in CUS CA, OR

11/30/1998 This association has been described reliably only from the eastern flank of the Bighorn Mountains of north-central W US SD, WY yoming. It may extend north 

11/1/1997 This association is naturally rare due to the specificity of its climatic and substrate requirements. It is restricted to marine terraces and headlands MX?, US CA, MXBC?

10/31/1997 This association has a naturally restricted distribution. Disjunct, scattered stands occur along approximately 150 miles of the north/south-trendinUS CA, NV

12/1/1997 US HI

11/7/1997 This association has an extremely limited range of distribution in the lower montane zone of the western slope of the southern Rocky MountainsUS CO

4/11/2006 This forested wetland is extremely rare within its range (confirmed to occur only in British Columbia, W CA, US? BC, OR?, WA ashington, and barely reaching into Oreg

10/23/1997 This riparian community is restricted to the east-central portion of the Columbia Basin of W US ID, OR?, WA ashington and in adjacent Idaho and Oregon. It is as

10/21/2002 There are 3 known occurrences in Oregon and an estimated 4 in W US OR, Washington. Remnant stands probably occupy less than 100 acres. This assoA

10/12/1997 The association has a restricted range of distribution and few high-quality examples have been located in that range. Most stands of this associaUS ID, OR, WA?

3/29/1999 While very little is known about the abundance and distribution of this association, it is clear that it is very rare and very threatened. Few examplUS CA?, ID?, NV?, OR, WA 

11/7/1997 This association has only been documented from a small region of the southern Rockies in south-central Colorado. Dams, water diversion, or exUS CO

1/6/2000 This is a very rare, valley bottom, riparian forest known only from the W US OR allowa River valley in northeastern Oregon. No examples are protected; 

12/1/1997 US HI

12/1/1997 US HI

12/1/1997 US HI

12/1/1997 US HI

12/1/1997 US HI

12/1/1997 US HI

12/1/1997 US HI

12/5/2000 This forest association has only 3 known viable occurrences covering about 500 acres in a very restricted range in the Olympic rainshadow of thUS WA 

11/14/1997 This community has a somewhat restricted natural range and occurs in very specific environments in portions of the Puget Lowland and Georgia CA, US BC, WA 

11/14/1997 Three to seven examples of this type are documented. The distribution of sites that could possibly develop examples of the type are restricted to US WA 

10/28/1997 This community has a restricted natural range in the rainshadow of the Olympic Mountains of W US WA ashington and occurs in a very specific environm

10/21/1997 This association is known only from the southern Animas Valley in the "Borderlands" of southwestern New Mexico. The only known occurrence US NM

11/30/1998 This community has a narrow natural range in the southeastern Cascade foothills in W US WA ashington and perhaps adjacent Oregon. This is a mid- to 

11/30/1998 This community has a highly restricted range in the southeastern Cascade foothills in W US CA, OR, WA ashington and adjacent Oregon, and is reported form no

11/14/1997 This type is restricted geographically to the eastern end of the Columbia River Gorge and adjacent foothills of W US OR?, WA ashington and possibly Oregon

11/30/1998 This community has a narrow natural range found along the southeastern Cascade foothills in W US OR, WA ashington and adjacent Oregon. This is a xeric 

11/17/2000 This forest association may have been a naturally rare type. It now has only 4 viable occurrences covering less than 500 acres in a very restricteUS OR, WA 

10/28/1997 These riparian woodlands are restricted to a unique transition zone between the Mojave and Great Basin deserts along three streams originatinUS UT

12/1/1997 US HI

12/1/1997 US HI

11/14/1997 This community has a restricted natural range in the rainshadow of the Olympic Mountains and Vancouver Island and occurs in a very specific eCA, US BC, OR, WA

11/14/1997 This community has a restricted natural range in the rainshadow of the Olympic Mountains and Vancouver Island and occurs in a specific enviroCA, US BC, WA

1/30/2007 This association is very rare, with very few known occurrences and a very limited area. It probably was previously significantly more numerous pUS WA

10/21/2002 his mid-seral to climax association is restricted to the northern coast of Oregon. It was probably never common and may have only occurred at tUS OR 

2/1/1996 US? ID?

6/2/2005 These riparian communities are restricted to coastal British Columbia, Canada, and occupy a relatively small portion of the landscape (linear sysCA BC

9/19/2005 This long-lived coniferous forest occurs as small patches within a very limited distribution (within 20 km of the coastline). Detailed ecosystem maCA BC

6/2/2005 This plant community is restricted to estuarine systems along the central coast of British Columbia, Canada. Element Occurrences are small anCA BC

1/30/2006 This matrix coniferous forest once dominated the landscape within its range. Old, structurally complex stands with gaps and vertical heterogeneCA, US BC, WA

9/19/2005 This matrix forest community occurs within a limited range. These once extensive old forests have been harvested over much of their range. HaCA BC

6/3/2004 This association is considered endemic to the central interior of British Columbia. This medium- to large-patch plant community is restricted to a CA BC

6/2/2005 This woodland community has a limited range, occurring only on ridge crests and hilltops on the south coast of British Columbia, Canada, at eleCA BC

4/11/2006 This forested community forms part of the forest matrix within its range. It is confirmed to occur only in British Columbia. It has experienced a suCA BC

9/19/2005 This productive forest has been harvested in the past and continues to be targeted. The long-term decline is considered to be moderate, but pacCA BC 
4/11/2006 This forest is confirmed to occur only in coastal British Columbia and W CA, US BC, WA ashington. It is rapidly declining in the short term with substantial decline 

9/19/2005 This matrix coniferous old forest has been substantially reduced due to past harvesting. Approximately one-third of these forests have been conCA BC

9/19/2005 Widely distributed but not extensive within its range, this old forested community has experienced a substantial decline over the long term. It conCA BC

6/2/2005 This community is restricted to the Queen Charlotte Islands of British Columbia, Canada, where it is subject to harvesting and alteration of vegeCA BC

9/19/2005 This forested community is uncommon within its range, and detailed ecosystem mapping indicates a large proportion of this community has beeCA BC

9/19/2005 The forested community, a significant component of the matrix forest, occurs within a limited range of the coast-interior transition region of BritisCA BC

9/19/2005 This small-patch forested plant community has a limited range in the coastal-interior transition of British Columbia. It has been extensively harveCA BC 

9/19/2005 This open forested community is widespread throughout its range but limited to sites with shallow soils or dry glaciofluvial outwash plains. It is in CA BC

3/30/2007 This is a small-patch community that is restricted in known distribution to seven occurrences in the Allegheny Mountains region of W US WV est Virginia

3/30/2007 This is a small-patch type that is restricted in known distribution to three occurrences (12 patches) within the Allegheny Mountains region of W US WV es

2/16/2007 Despite considerable efforts to inventory this community over the years, fewer than 50 patches of this vegetation are known covering an aggregUS MD?, VA

12/3/1998 This freshwater tidal swamp community is restricted to the freshwater tidal portions of rivers in Massachusetts, New York, and New Jersey. Size US CT, DE?, MA, NJ, NY

6/8/2004 US NJ

6/10/2004 <i>Rhododendron maximum</i> and <i>Chamaecyparis thyoides</i> overlap in range from New Jersey to New Hampshire. Limited occurrences US CT, NH, NJ, NY, RI

11/16/1997 There are probably 30-60 occurrences of this community rangewide. At least 19 occurrences have been documented from Connecticut, MassacCA?, US CT, MA, ME?, NH, NJ, NY, ON?, PA, VT

11/15/1997 This community is known from upstate New York, southwestern Vermont, southeastern Ontario, and Rhode Island. There are probably fewer thaCA, US CT, MA, NY, ON, RI, VT

11/18/1997 This maritime woodland community is naturally restricted to major coastal dune systems. An estimated maximum of 30 occurrences exist, rangiUS CT, DE, MA, MD, NJ, NY, VA

12/1/1997 US MD, NC, NY, PA, TN?, VA?, WV

3/30/2007 This is a small-patch community that is restricted in known distribution to six occurrences within the Allegheny Mountains region of W US WV est Virginia

4/4/2007 This is a small-patch type that is restricted in known distribution to six occurrences within the Allegheny Mountains region of W US PA, WV est Virginia and to 

3/30/2007 This is a small-patch community that is restricted in known distribution to five occurrences in the Allegheny Mountains region of W US WV est Virginia. It 

4/30/1998 US NJ, NY

1/18/2006 US DC, MD, NJ

1/31/2007 This coastal woodland of acidic rocky outcrops is restricted to southern Maine, with outliers in eastern New York. An estimated 20-30 occurrenceUS ME, NY

1/31/2007 This maritime woodland community is restricted to major coastal sand dune systems. It ranges from southern Maine to Cape Henlopen, DelawaUS DE, MA, ME, NJ, NY, RI?

1/31/2007 This association has fewer than 20 occurrences, with a total rangewide acreage of fewer than 10,000 acres. The range of this association is resUS NJ

4/30/1998 US NJ, NY

11/17/1997 There are fewer than 20 occurrences of this community rangewide, and many are severely degraded small remnants. This community is dependUS CT, MA, NH, NY, PA, RI

12/10/1998 There are fewer than 20 occurrences of this community rangewide; it is only known from southeastern Maine and south-central New HampshireUS ME, NH 

11/19/1997 There are probably fewer than 10 occurrences rangewide. Currently fewer than 5 occurrences are known from New Hampshire, with a total of leUS MA, NH

6/10/2008 This coastal forest is limited to the immediate vicinity of the coast in southern New Jersey, Delaware, Maryland, and Virginia. EO Rank EstimatoUS DE, MD, NJ, VA

10/5/2006 This community is restricted to very specific environmental conditions on high-gradient rivershores with a combination of control by bedrock and US DC, DE, MD, VA, WV?

10/12/2004 US MD?, NJ, PA?

1/31/2007 This maritime forest community is restricted in range to the coastal areas of seven northeastern states. Average occurrence size is estimated to US CT, DE, MA, ME?, NH, NJ, NY, RI

11/17/1997 This community is known from the Ridge and Valley physiographic province in west-central Virginia. There are probably fewer than 20 occurrencUS VA

5/31/2007 This association occurs in small patches and has high environmental specificity. There are probably fewer than 100 occurrences rangewide, and US MD, PA, VA, WV

9/9/1999 Currently there are seven occurrences documented from North Dakota; the community is also reported from W US ND, SD, WY yoming, and possibly South Dak

6/22/1998 Few occurrences have been documented. The range of this woodland community is restricted to slopes and rolling topography in the northern GCA, US MB, ND, SK

6/22/1998 There are probably fewer than 25 occurrences of this community rangewide; it is only known from central Indiana, where it is ranked S2, and froCA?, US IN, MI, OH, ON?

11/13/2006 There have been 155 occurrences documented: 3 in Illinois (where the community is ranked S4) (but beech-maple is only a small part of the IllinCA, US IL, IN, MI, NY, OH, ON

6/22/1998 There are probably fewer than 100 occurrences of this community rangewide. Currently 23 occurrences are documented from Indiana (where it CA, US IN, KY, MD, OH, ON, PA?, TN?

6/22/1998 There are probably fewer than 100 occurrences of this community rangewide. It is reported from Montana (where it is ranked S1Q), North DakotUS MT, ND, NE, SD

10/24/2002 This community occurs in isolated patches across the central Great Lakes region, from southern Minnesota east to south-central Michigan and sCA, US IN, MI, MN, OH, ON, WI

6/22/1998 There maybe fewer than 100 occurrences in the Black Hills, its only known location. US SD, WY

9/1/1999 This type has only been reported from the Black Hills, where it is locally abundant in higher-elevation streams. Nine A-B quality EOs were identifUS SD

12/31/1998 This type probably occurs scattered through the Great Lakes region in southern Ontario, northern Michigan, and northern New York, but it has nCA, US MI, NY, ON

10/23/2002 There may be fewer than 100 occurrences of this community rangewide; it is reported from Missouri (where it is ranked S3 to S4S5), Arkansas (US AR, MO, OK

6/22/1998 This type has a naturally restricted distribution. McIntosh (1950) mentioned that some of the more accessible stands in his study had been loggeUS IA, MN, WI

2/6/2007 There are probably fewer than 20 occurrences from a restricted range. Four occurrences have been documented in two states (Minnesota and W US MN 

2/27/2000 The distribution and extent of this community are limited. Sites are prone to invasion by brush and exotic weeds in the absence of flooding or as US CO, KS, NE, OK, SD?, TX

6/22/1998 The total number of occurrences is unknown. Thirteen have been documented in North Dakota, where the community is ranked S1S2?. AlthougUS CO, MT, ND, SD, WY 

6/22/1998 Only a few occurrences of this community are known. Most of the original sites have been destroyed by logging, grazing, conversion to forest beUS AR, IL, IN, MO
6/22/1998 This type may have a restricted distribution within the lakeplain of the Great Lakes. Many sites have been converted for agricultural developmen

CA, US MI, ON

6/22/1998 This community has been highly degraded in the mesic sites where it occurred historically. Bur oak woodlands and forests have recently spread US IA, KS, MO, NE, SD

6/22/1998 There are probably fewer than 50 occurrences of this community rangewide. It has a restricted distribution in a predominantly prairie landscape; CA, US ND, SK

9/9/1999 Most <i>Quercus macrocarpa</i>-dominated stands in the Black Hills are heavily grazed (Hoffman and Alexander 1987). US SD, WY

6/22/1998 This woodland type has a relatively restricted distribution in a predominantly prairie landscape. Remaining occurrences have been logged, grazeUS IN, KS

3/31/2000 There may be less than 20 occurrences of this community rangewide. It is reported from southwestern Indiana (where it is ranked S1), southern US AR, IL, IN, KY?, MO, TN?

6/22/1998 There are probably fewer than 100 occurrences of this community rangewide. It is reported from Ohio (where it is ranked S3), Indiana (S2), IllinoCA, US IL, IN, MI, OH, ON

6/22/1998 There are probably fewer than 100 occurrences rangewide. Eighteen occurrences have been documented from 3 states (Illinois, Indiana, and MCA, US IL, IN, MI, MO, OH, ON

3/31/2000 There are probably fewer than 50 occurrences of this community rangewide. Currently only one occurrence is documented from Missouri. It is reUS AR?, IL?, IN?, KY?, LA?, MO

6/22/1998 There are probably fewer than 100 occurrences rangewide. Currently 29 occurrences have been documented in Missouri where it is ranked S2; US AR, IL, IN, MO, OK

6/22/1998 There are probably fewer than 50 occurrences of this community rangewide. Currently 23 occurrences have been documented in Illinois, IndianaUS AR, IL, IN, KY, MO

6/22/1998 There are probably fewer than 100 occurrences of this community rangewide. It is reported from Minnesota (where it is ranked S2), W CA, US MI, MN, ON, WI isconsin (

8/4/1998 There are probably fewer than 50 occurrences of this community rangewide. It is restricted to north-facing calcareous bedrock cliffs and summitUS KY, MD, OH, PA, TN, VA, WV 

2/6/2007 There may be fewer than 20 occurrences of this community rangewide. It is only known from W US WI isconsin (where it is ranked S2). There are curre

1/31/2002 This longleaf pine woodland community is restricted in range and habitat conditions. It only occurs in eastern Texas and western Louisiana on nUS LA, TX 

1/21/2000 This longleaf pine woodland community is restricted in range and habitat conditions. It only occurs in eastern Texas and western Louisiana on nUS LA, TX 

8/11/1997 This saturated longleaf pine - pond pine woodland association is found in a restricted range and specific set of habitat conditions. It occurs only US NC, SC

12/11/1998 This mesic forest is restricted in range and occurs only in a specific set of substrate and habitat conditions. It is apparently restricted to moist, noUS AR

12/11/1998 This association is restricted to a few mesic limestone canyon systems in the Boerne area of Kendall County and several locations in Bandera, US TX

12/21/1999 This association is naturally restricted in range and environmental setting. It is found only in the most mesic canyons in the Guadalupe MountainUS TX

1/17/2001 This community type is documented from the south-central North Carolina Piedmont, and appears to be relatively restricted in distribution and eUS NC

1/2/2002 This vegetation is so far known only from sandstones of Mount Magazine in the Ouachita Mountains of Arkansas, where it is restricted to habitatUS AR

12/16/1999 This community is restricted in its geographic distribution and occurs in a very specific land type and environment. This vegetation occurs at the US IL?, KY, TN

12/8/2000 These Appalachian seeps occupy very small areas (1-10 acres) and are threatened by forest clearing, agricultural effects, residential developmeUS KY, TN

12/14/1998 This community represents rare seepage bogs in the lower Piedmont of North Carolina. These seepage bogs apparently occurred in a landscapUS NC

1/13/1998 PR, US FL

12/1/1997 MX?, US TX

1/22/2008 This community is scattered throughout the high mountains but is fairly uncommon. Unlike many other forest types in the Southern AppalachianUS GA, KY?, NC, TN, VA?

10/27/2003 This community is scattered throughout the high elevations of the Southern Blue Ridge with highly localized outliers also found at the highest eleUS GA?, NC, TN, VA, WV

6/21/2001 This is a small-patch community type occupying very restricted habitats within a narrow geographic range. There are less than 20 known occurrUS VA, WV

12/14/1998 This community is limited to regionally uncommon and small exposures of moderately nutrient-rich rock in the Southern Blue Ridge, and is thougUS GA, NC, TN, VA?

10/23/2002 This community is limited to regionally uncommon and small exposures of moderately nutrient-rich rock in the Southern Blue Ridge (and possibUS TN, VA

1/23/2000 This community is restricted to high base status soils derived from coquina or other limestone outcrops or more recent shell deposits in the outeUS GA?, SC

6/29/2001 US AL, FL?, GA?, MS?

1/10/2008 This saturated forest association is found along the margins of streams or seepages in the Fall-line Sandhills area of North Carolina, South CaroUS GA, NC, SC

12/31/1997 This saturated forest association is restricted to the East Gulf Coastal Plain of Mississippi, Florida, and possibly Alabama; it occurs in a specializUS AL?, FL, MS

5/15/2002 This association is limited to north-central Florida, and a specific saturated, high-pH substrate. US FL

12/31/1997 This saturated sparse woodland is restricted to "steephead streams" in the Florida Panhandle and adjacent Alabama. It has a restricted distribuUS AL, FL 

11/21/1997 This saturated forest association occurs in isolated populations in northeastern Florida and in more extensive but discontinuous stands along the US AL, FL, MS

6/10/1997 This saturated forest association is restricted to the Atlantic Coastal Plain of Virginia, North Carolina, and possibly South Carolina; it occurs in a US NC, SC?, VA 

9/13/1997 US FL

12/11/1998 This mayhaw pond association occurs in sinkholes and other isolated upland depressions of the South Atlantic and East Gulf coastal plains of GUS FL, GA

3/29/1999 This mayhaw pond association is restricted to isolated seasonal depression ponds found only in southwestern Georgia, southeastern Alabama, US AL, FL, GA

1/2/2001 Naturally geographically restricted to the West Gulf Coastal Plain and naturally uncommon, this type was historically found in only small patches US LA, TX 

12/28/2000 This type is restricted to small perennial stream bottoms within the range of <i>Pinus palustris</i>, including the central and eastern Florida pariUS LA, MS?

11/23/1997 US FL?, GA, SC

10/3/2001 This association is only known from a very restricted area in Alabama. US AL

12/19/1997 This community is vulnerable to logging (selective removal of mature <i>Pinus glabra</i>) and fragmentation due to housing development. US FL

2/23/2004 This forest occurs within a narrow geographic range that includes limited portions of western Kentucky, Tennessee, northern Mississippi, and eaUS AR, KY, MS, TN

1/12/2001 This association occurs in a small geographic area and is further limited by the paucity of calcareous / subcalcareous substrate. It has been subUS AR?, LA, TX 

2/22/2007 This heath bluff association is restricted to steep north-facing slopes in the lower Piedmont and upper Coastal Plain of North Carolina and other US AL, GA?, NC, SC?, VA

3/30/2004 This community is naturally rare, geographically restricted, and confined to special edaphic habitats, primarily over metabasalt in the Blue Ridge US MD, VA, WV 
12/11/1998 This community is known from only 5-10 sites, where it occurs in areas of 10 to about 250 acres. All known sites are on Piedmont granite domes 

US GA, NC 

9/30/2004 This association is restricted to the Florida Panhandle, with possible occurrences in Alabama and Georgia. Very few examples are protected. DUS AL?, FL, GA?

8/15/1997 US FL

1/29/2001 This association occurs as scattered wetland inclusions in second bottoms and Pleistocene terraces. It is naturally very restricted in range and eUS LA, TX

11/8/1999 The global range of this association has yet to be clearly delimited. It is thought to be restricted to the Columbia Bottomlands area of the coastaUS TX

12/8/1999 This association is known only from upland ponds of the Macon Ridge in the Mississippi River Alluvial Plain (MSRAP) of northern Louisiana that US AR?, LA

6/8/1998 US SC

12/27/1999 This vegetation has a naturally restricted range of distribution, being limited to dry limestone rocky areas in the Eastern Knobs region of KentuckUS KY

1/31/2001 The extent of this bay forest is poorly understood, but it appears to be rare and of restricted distribution. US FL, GA, SC?

10/3/1996 US OK

12/11/1998 This association is naturally rare, being restricted to specialized edaphic conditions (thin soil over dolomite) on the Springfield Plateau and possUS AR, MO, OK? 

1/2/2001 This association is restricted to rimrock bluffs and cliffs in the Ozark Highlands of the United States, ranging from Missouri to Arkansas and OklaUS AR, MO, OK 

1/16/2001 This community is naturally rare because of the relative rarity of the edaphic conditions on which it depends. Examples on isolated islands remaUS FL, GA, NC, SC

12/14/1998 This is apparently a natural community, occurring after abnormally long periods of fire exclusion or in especially fire-protected situations in the nUS AL, MS

12/15/1999 This vegetation has a naturally restricted range of distribution, being limited to dry limestone rocky areas in the Bluegrass Basin and related areaUS KY, TN

12/29/1998 This community type occurs in small areas and is apparently restricted to more nutrient-rich or siltier portions of the southeastern Coastal Plain. US FL, GA?, SC

12/14/1998 This <i>Maclura pomifera</i>-dominated riparian mesic blackland community occurs in deep soils on level terrain, typically as relatively narrow US AR, TX? 

10/20/1996 US AL, LA, MS

1/22/1998 This seepage-fed saturated evergreen forest is restricted in its range and in the topographic situation in which it occurs. It is restricted to the FloUS FL

1/10/1998 This community has a restricted distribution with less than 1214 ha remaining (Kruer 1992). Most remaining examples have been impacted by eUS FL

1/10/1998 This community has a restricted distribution with about 2023 ha remaining (Kruer 1992). Most remaining examples have been impacted by exotiUS FL

1/9/2001 The specialized habitat required for this community is scarce. It is restricted to floodplain edges of brownwater floodplains in the South Atlantic aUS GA, SC

1/31/2001 Nonriverine swamp forests of the mid-Atlantic Coastal Plain have been severely impacted by forestry and agricultural conversion. This particular US NC, VA?

2/4/1999 Apparently very rare. US LA, TX?

1/31/2007 This is a nonriverine swamp forest which occurs in a very limited area of habitat in the North Carolina Coastal Plain. It occurs on mineral soils, in US NC, VA?

3/29/2001 This association seems to be floristically distinct from related types to the north and south, but its complete range is not known. US AL, MS

6/23/1997 US FL

6/23/1997 US FL

6/19/1997 Hydrologic alterations are the biggest threat to this type. Past ditching and draining have altered many examples. ORV traffic also poses a threaUS AL, FL, GA? 

3/28/2001 This association is restricted to sinkhole depressions in the Coastal Plain of Florida and Georgia. US FL, GA

1/17/2001 This association is naturally rare, being limited to unusual sinkhole ponds in the southeastern Coastal Plain. It occurs in isolated depressional wUS GA, SC

4/30/1998 This community is restricted to the highest mountain systems of the southern Appalachians in eastern Tennessee, western North Carolina, and US NC, TN, VA 

1/4/2000 The community is geographically and environmentally restricted to the highest elevations of the Southern Blue Ridge. Very few occurrences are US NC, TN

3/15/2005 This and related vegetation types are environmentally restricted within a somewhat geographically restricted range. Their former extent has beeUS NC, TN, VA, WV 

6/26/2001 This vegetation type is geographically and environmentally restricted, and its former extent has been reduced to more or less isolated, small patUS MD?, PA?, VA, WV

10/20/1996 MX?, US MXCO?, TX

12/11/1998 This association is restricted in the United States to higher elevations in the Chisos Mountains in Brewster County, Texas, where all known examMX?, US MXCO?, TX

12/11/1998 This association is restricted in the United States to higher elevations in the Chisos Mountains in Brewster County, Texas, where all known examMX?, US MXCO?, TX

1/17/2001 This community type is apparently limited edaphically to a relatively narrow elevational (and moisture) range in the Davis Mountains of western TUS TX

10/20/1996 MX?, US MXCO?, TX

10/20/1996 US TX

1/10/1998 This community is restricted to the Florida Peninsula. The largest occurrences are found in Ocala National Forest, in central Florida. Fire regimeUS FL

11/23/1997 This Sand Pine woodland association is restricted to a particular soil type and topographic situation in the Gulf Coastal Plain of Panhandle FloridUS AL, FL

11/22/1997 This sand pine woodland association is an interior scrub association of the Coastal Plain of Florida not restricted to coastal situations. It is found US FL

10/22/2002 This association is naturally restricted in range and environmental setting to mafic rock outcrops in northern Georgia. The degree of uncertainty US GA

10/22/2002 This forest remains poorly understood and poorly documented, possibly because it has included a number of different concepts from different geUS AR, LA, OK?, TX 

6/10/2004 This xeric shortleaf pine forest/woodland is endemic to the Coastal Plain west of the Mississippi River. Although a few examples are known on UUS AR?, LA, OK, TX

2/11/2004 This prairie woodland is very rare throughout a rather limited range in the Coosa River Valley in northwestern Georgia and northeastern AlabamUS AL, GA

10/23/2002 As currently defined, this association is restricted the Coastal Plain west of the Mississippi River. In most of the region shortleaf pine forests havUS AR, LA, OK?, TX

10/22/2002 This community is associated with upper, often west-facing, slopes with extreme exposure. It is apparently limited in its occurrence. It is definitelUS NC

10/22/2002 The type is known only from one general area on Pine Mountain (in the Cumberland Mountains on the Virginia-Kentucky stateline), where it occUS KY?, VA, WV?

10/22/2002 High-quality examples of this community are rare throughout its range, most sites having been chronically fire-suppressed, resulting in a loss of US AR, MO, OK
10/22/2002 As currently conceptualized, this association differs from most other extremely xeric types of the region due to occurrence on stream terraces. X

US AR?, LA, TX? 

10/3/2001 This association is restricted to a limited number of large blackwater streams and rivers in western Florida and southern Alabama where <i>ChaUS AL, FL

11/23/1997 This saturated slash pine woodland association is restricted to the central Florida peninsula. The remaining examples, which are not on public laUS FL

1/10/1998 This community is restricted to the tropical southwestern tip of the Florida peninsula. Though highly restricted in distribution and extent, the comUS FL

1/10/1998 This community is restricted to the southwestern tropical tip of the Florida peninsula. Though highly restricted in distribution and extent, the comUS FL

6/25/1997 This upland barrier island slash pine woodland association is found in a restricted range and specific set of habitat conditions. This association iUS AL, FL, GA, LA, MS, SC

11/23/1997 Nearly flat seepage areas in landscape of slash pine flatwoods, with open canopy of <i>Pinus elliottii var. elliottii</i> and <i>Pinus serotina</i>. TUS AL?, FL, GA, MS

10/15/1996 US AL?, FL, LA, MS

1/17/2001 This association is naturally restricted to wet flatwoods of the South Atlantic Coastal Plain, and possibly the East Gulf Coastal Plain, of Georgia. US FL?, GA, SC?

1/24/2000 This association is naturally restricted to wet flatwoods of the East Gulf Coastal Plain. It is currently known only from Louisiana but probably occUS AL?, LA, MS

2/1/2001 This saturated <i>Pinus elliottii</i> acid swamp association is restricted to the East Gulf Coastal Plain. The remaining examples which are not oUS AL?, FL, MS?

1/10/1998 This community is apparently rare, being restricted to swamp islands. The community has been reduced in extent and quality by logging. ExampUS GA, SC?

10/23/2002 This longleaf - slash pine community is restricted to the southern Florida peninsula, where it is documented from Myakka River State Park. Its oUS FL

1/24/2000 This longleaf pine woodland association is apparently restricted in distribution to eastern Georgia. It is part of the endangered Longleaf Pine EcoUS GA

1/19/1999 This community is poorly understood, since few examples remain, and these are in poor condition. These communities are moist to wet longleaf US NC, VA

9/3/2002 As with all other longleaf pine types it is believed the areal extent has diminished since European settlement. It is threatened by alteration of fire US LA, TX

1/22/1998 The range of this longleaf pine - mixed pine community is limited to the dissected topography of the Southern Loessal Plains (East Gulf Coastal US MS

2/17/2004 This association was never common and has always been restricted to montane areas of the Ridge and Valley Province of Alabama and GeorgUS AL, GA, NC, SC?

10/10/1997 This saturated longleaf pine - pond pine woodland association is restricted in range and the substrate on which it occurs. It is a naturally rare typUS FL, GA

12/31/1997 This saturated longleaf pine - pond pine woodland association is restricted both in range and in the substrate on which it occurs. It is only found US NC, SC

12/31/1997 The canopy of this mixed pine woodland association is dominated by longleaf pine and loblolly pine. It is found only in a very restricted range anUS NC, SC

9/3/2002 This community is known only from very limited areas of eastern Texas; as with all other longleaf pine types it is believed the areal extent has diUS LA, TX

12/31/1997 This is a mesic longleaf pine woodland community, without scrub oaks, restricted to mesic soils in the middle and outer Coastal Plain of North CUS NC, SC

12/31/1997 This is a mesic longleaf pine woodland association is found in a restricted range and specific set of habitat conditions. It lacks scrub oaks and is US NC, SC 

8/11/1997 This saturated longleaf pine woodland community occurs in central to west-central Louisiana, possibly ranging into adjacent or related areas of TUS LA, TX?

12/31/1997 This saturated longleaf pine woodland community is very restricted in range, occurring only in Brunswick County, North Carolina, where it is the US NC

10/23/2002 This type is much less common than the <i>Quercus laevis</i> types of the same region (Clewell 1971). It is apparently restricted to the Munson US FL

10/23/2002 This type presumably occurs in 9 isolated patches or "islands" ranging in size from 60-4000 hectares, surrounded by sand pine-scrub vegetation US FL

1/31/2002 This longleaf pine woodland community is found only in a restricted range and under a specific set of habitat conditions. It only occurs west of thUS LA, TX 

12/17/1998 This longleaf pine woodland association is found in a restricted range and is susceptible to forest conversion. It is limited to the sandhills and innUS GA, SC

8/11/1997 This longleaf pine woodland association is found in a restricted range and is susceptible to forest conversion. It is limited to the Atlantic Coastal US GA

12/31/1997 This longleaf pine woodland association has an open canopy. It is restricted in distribution as well as in the topographic situations in which it occUS NC, SC 

9/3/2002 As with all other longleaf pine types it is believed the areal extent has diminished since European settlement. It is threatened by alteration of fire US LA?, TX

12/31/1997 This woodland community is restricted to the Fall-line Sandhills of South Carolina, a very narrow natural geographic range lying south of the distUS SC

12/31/1997 This xeric longleaf pine sandhill woodland association is found in a restricted range and specific set of habitat conditions. It occurs only in the ouUS NC, SC

12/17/1998 This longleaf pine woodland association is found in a restricted range and is susceptible to forest conversion. It is limited to the sandhills of the SUS FL, GA, SC

10/10/1997 This longleaf pine woodland community is restricted to sites that are so extremely xeric that <i>Aristida stricta</i> (in more northern examples) aUS GA, NC, SC

12/31/1997 This xeric longleaf pine sandhill woodland association is found in a restricted range and specific set of habitat conditions. It is one of the driest loUS NC, SC

12/31/1997 This longleaf pine sandhill woodland association is found in a restricted range and specific set of habitat conditions. It is part of the endangered US GA, SC

12/31/1997 This subxeric longleaf pine woodland community has a restricted distribution and is limited to a specific set of habitat conditions. It occurs on weUS AL?, FL, GA?, MS

12/31/1997 This xeric longleaf pine sandhill woodland association is found in a restricted range and specific set of habitat conditions. It occurs only in dry, saUS FL, GA

12/31/1997 This longleaf pine sandhill woodland community has a restricted distribution, being only known from the East Gulf Coastal Plain of Mississippi (aUS MS

4/19/2004 This longleaf pine woodland is known only from subxeric situations on upland ridges, knolls, and slopes of the Outer Coastal Plain of South CaroUS SC

10/10/1997 This longleaf pine sandstone outcrop woodland association is found in a restricted range and specific set of habitat conditions. It is known only fUS GA

12/31/1997 This longleaf pine / scrub oak sandhill woodland association is found in a restricted range and specific set of habitat conditions. It is distributed pUS NC, SC

12/31/1997 This longleaf pine woodland community is found only in a very localized range and under a specific set of habitat conditions. In addition, it is susUS LA, TX

10/23/2002 This longleaf pine community is restricted to the WUSest Gulf Coastal Plain, where it is currently known only from Texas. More information is needLA?, TX

10/27/2003 This longleaf pine woodland association is found in a restricted range and under particular habitat and soil conditions. It occurs on rolling upland US AL, MS

12/31/1997 This longleaf pine sandhill woodland association is found in a restricted range and specific set of habitat conditions. It is restricted to topographicUS NC, SC

4/19/2004 This saturated longleaf pine woodland association is restricted to South Carolina. A naturally rare and restricted community type, this longleaf piUS SC

10/23/2002 This type is described from Colquitt and Worth counties, Georgia. Like most longleaf pine communities, this type is seriously imperiled because US FL?, GA

12/14/1998 This is a West Gulf Coastal Plain wetland longleaf community, occurring on non-saline soils of the Prairie and Intermediate Terraces of LouisianUS LA, TX
1/22/1998 This longleaf pine woodland community is restricted to the East Gulf Coastal Plain of eastern Louisiana and likely also adjacent southwestern M

US LA, MS?

11/23/1997 This mesic longleaf pine woodland community occurs on gently rolling topography over moderately well-drained silt loams and fine sandy loams US LA, TX 

1/30/2003 This longleaf pine association is restricted to coastal terraces of the Florida parishes of Louisiana where it is found on upland rises in flatwoods lUS LA, MS?

12/31/1997 This longleaf pine woodland community occurs west of the Mississippi River in west-central Louisiana and eastern Texas, particularly on the W US LA, TX i

12/31/1997 This longleaf pine woodland association is found in a restricted range and specific set of habitat conditions and is susceptible to forest conversioUS LA, TX 

10/10/1997 This broadly defined saturated longleaf pine woodland association is a moderately to poorly drained longleaf flatwoods, widespread in Florida, aUS AL, FL, GA, MS?, SC

5/3/1997 This longleaf pine woodland association is found in a restricted range and specific set of habitat conditions. It is restricted to sandy, mesic to moUS FL, GA, SC

1/21/2000 This association is naturally very restricted in range and environmental setting. It is currently known only from the highest elevations of the GuadMX?, US TX 

12/11/1998 <i>Pinus remota</i> ranges across a four- or five-county area in the southwestern quarter of the Edwards Plateau, but only in a few areas is it a US TX

10/20/1996 MX?, US TX

1/21/2000 This community is endemic to the Southern Blue Ridge where it occurs on high-elevation ridges (over 1220 m [4000 feet]). It is maintained by peUS NC, TN?, VA?

10/4/2004 This association is limited to a specific aspect in a small area near the Kentucky-Virginia stateline. Threats include pine beetle damage and succUS KY, VA?

10/4/2004 This association is limited to a very specific landscape setting, where it occurs in small patches. Threats include drainage and intensive pine foreUS NC, SC, VA?

1/8/2007 This association is limited to a very specific landscape setting. Threats include drainage and intensive pine forestry management (i.e., bedding, US FL

8/11/1997 This saturated pond pine woodland association is found in a restricted range and specific set of habitat conditions. It is restricted to the Dismal SUS NC, VA

12/31/1997 This saturated pond pine woodland association is found in a restricted range and specific set of habitat conditions. It is a strange type of pocosinUS NC, SC?, VA?

5/16/2002 These woodlands are only documented from Apalachicola National Forest. This association may occur at numerous locations on Apalachicola aUS FL

1/4/2000 This community is geographically restricted and uncommon within its range. US GA, NC, SC, TN

7/14/2000 This type has a very narrow geographic range, and is further limited both topographically and edaphically. This type as described should be at leUS AR?, LA, OK, TX

12/1/1997 US NC, VA?

6/20/1997 US DE, MD?, VA

1/31/2001 This community is apparently rare, being restricted to sites on sandy levees and swamp islands naturally protected from fire by wetter surroundiUS FL, GA, NC, SC

8/15/1997 US NC, SC

2/19/2004 As defined, this community is limited to the rare outcrops of shale in the Blue Ridge and in the transition between the Blue Ridge and Ridge and US NC, SC?, TN 

2/23/1999 This community is naturally uncommon in the Southern Blue Ridge. W US GA?, NC, SC, TN ell-developed examples are rare due to clearing for agriculture and develo

12/14/1998 This association is limited to heavy saline soils in close proximity to the coast of extreme southern Texas and Tamaulipas. Threats are high, espMX, US MXTM, TX

6/12/2001 Only a small percentage of the original acreage of this community remains. Unprotected examples are threatened by residential and industrial dMX, US MXTM, TX

1/31/2007 This vegetation has a naturally restricted range of distribution, being limited to The Barrens of the southeastern Highland Rim of Tennessee. MoUS TN

12/4/2003 This is a very uncommon association, and examples are known only from the Ridge and Valley of Georgia and (presumably) Alabama. Very few US AL, GA

8/15/1997 This association is restricted to special wetland habitats and was probably never common on the landscape. However, extensive areas of suitabUS VA

10/15/1996 US GA?, NC

10/4/2004 This association is known as a matrix forest type in the area of Brevard, North Carolina, where it occurs on open slopes and broad ridges in a laUS GA?, NC, SC?, TN?

2/25/2004 This community is restricted to a portion of the West Gulf Coastal Plain that lies outside or along the natural range limits of several typically soutUS LA?, TX

1/31/2001 This forest type is limited to mafic rock substrates in the Piedmont of North Carolina and possibly South Carolina. This type was probably naturaUS NC, SC?

1/3/2001 This forest is restricted in range, and its occurrences are limited to soils derived from mafic rocks. All known occurrences are on mafic members US AL?, GA, NC, SC

2/25/2004 This community is restricted to the West Gulf Coastal Plain. At present it is known only from Texas but could occur in Louisiana. The ? on the raUS LA?, TX 

12/29/1999 This forest is restricted geographically, and if considered distinct, it is naturally rare within its range. It is floristically related to other, more commUS GA, NC, SC, TN

12/31/1997 This xeric oak woodland community has a restricted distribution with few known occurrences. It is only known from the W US AR, LA, TX? est Gulf Coastal Plain 

10/12/1997 US OK

1/31/2001 This calcareous Outer Coastal Plain community is apparently rare and restricted to unusual edaphic sites in coastal areas of North Carolina and US NC, SC 

1/31/2007 This is an unusual upland wetland community, never abundant in the landscape and severely impacted by agriculture and other intensive land uUS IN?, KY, MS, TN

11/4/1997 US OK, TX?

5/23/2001 This community is naturally restricted to deep sands of Pleistocene barrier islands in a few counties along the Texas Gulf Coastal Bend. Its shadUS TX 

1/10/1998 This community is of very limited extent. It has been strongly affected by coastal development and fire suppression. US FL, GA

5/15/2002 This community is limited to central Florida. US FL

1/22/1998 This xeric maritime hammock community of the Florida panhandle coast (and possibly adjacent Alabama) is of very limited extent. It has been sUS AL?, FL

2/11/2004 This type is confined to a small natural region of the East Gulf Coastal Plain. It is found in the outer portions of this region relatively close to the US AL?, FL, MS 

5/20/2002 This association is limited to slopes in central Florida. US FL

12/1/1999 This dry-to-mesic hardwood forest is dependent upon well-drained slopes of seepage streams and steepheads in the northwestern Florida portioUS FL, GA?

1/22/1998 This evergreen forest is restricted to fire-sheltered topographic situations, in particular swamp islands in the outer and middle Coastal Plain of NUS GA, NC, SC

1/4/2001 This forest association is restricted to fire-protected islands of high ground surrounded by riverine swamps, and on slopes and bluffs where protUS FL, GA, SC?

12/15/1994 This open woodland occurs as small stands, generally less than 10 ha, and is often interspersed with grassy openings. It is restricted to rocky caUS TX
12/10/1999 This naturally rare association is only known from a restricted set of environmental conditions. It is a component of the endangered Longleaf Pin

US AL, LA, MS

6/14/2001 Because of drainage of habitat for these forests, they are much less plentiful than they probably were in the past. US GA, NC, SC, VA?

12/16/1999 This association is restricted in distribution to the Pennyroyal Karst Plain of the Highland Rim of Kentucky and Tennessee. This area has largely US KY, TN

1/8/2001 This type was always likely rare, given the unique habitat that it is found in. It is restricted to wet depressions in eolian sand deposits, in the wesUS AR, MO

12/13/1999 This association is only known from second terraces of antecedent courses of the Red River in northwestern Louisiana and possibly Arkansas. UUS AR?, LA, TX?

1/3/2001 While incompletely known and defined, this association is restricted to isolated locations at the edge of the range of the primary nominal oak (<i>US AR, MO

10/23/2002 This woodland (formerly wooded herbaceous) association is found in a restricted range and specific set of habitat conditions. It only occurs in baUS AL?, KY?, TN 

12/4/1999 This relatively rare hardwood-loblolly forest occurs on flats of the Pleistocene Prairie Terrace of the Louisiana East Gulf Coastal Plain. Threats inUS LA

10/24/2002 This unusual forest association is restricted to areas with saturated rather than temporarily flooded hydrology. It generally occurs in association US NC, VA

1/3/2001 This is an unusual forested association with saturated rather than temporarily flooded hydrology. The specialized habitat required for this commuUS GA?, NC?, SC, VA?

9/5/2008 This association has a relatively restricted range, being limited to the Interior Low Plateau region of the eastern United States. It occurs on large US AL?, IN?, KY, TN?

1/31/2008 This association is known only from the Upper Atlantic Coastal Plain of Georgia and is limited to exposures of limestone in a blackland prairie laUS GA 

10/23/1997 US TX

10/21/2003 This community may be of limited extent. Its distribution is not known. US FL, GA?

4/21/2004 US SC

12/13/1999 This association is restricted to slowly permeable, relatively poorly drained silt loam soils overlying loess deposits associated with the MississippUS LA

12/29/1998 This community appears to be rare, being restricted to wet flats in the outer Coastal Plain of South Carolina and possibly Georgia. It was probabUS GA?, SC

8/22/1997 This association is restricted in range, being largely restricted to Triassic basins of the Piedmont (Southern Triassic Basins Subsection 231Ao). US NC, SC?, VA

5/29/2007 In evaluating the global status of this unit, six ranking criteria of approximately equal weight were used: (1) Estimated number of occurrences: <3US MD, VA

12/14/1998 High-quality occurrences of this type are rare. Many occurrences have been subjected to logging, drainage, and damming. US AR

1/31/2007 This wetland forest type is restricted to the barrens of Tennessee's southeastern Highland Rim, where this vegetation develops in upland depresUS TN

2/2/1999 As currently circumscribed, this community type is known only from limited areas of eastern Texas. Although it may occur in Louisiana, it has yeUS AR?, LA?, TX 

1/25/2001 This was never a common community. The small size of examples and their poor drainage for development and economic uses make them a bUS AL, DC?, GA?, MD, NC, SC, VA

5/31/2001 This deciduous forest association is naturally very restricted in range and environmental setting, being restricted to mafic substrates in the PiedmUS GA, NC, SC?

1/2/2001 This deciduous woodland association has a restricted distribution with few known occurrences. It is restricted to xeric sandstone and acid shales US KY, TN?, WV?

4/30/1998 This community is relatively secure within its range, but has a naturally restricted habitat. Red oak decline is affecting occurrences of this commUS NC, TN, VA?

6/10/2004 This community has a restricted natural range along the southeastern escarpment region of the Southern Blue Ridge of North Carolina and GeoUS GA, NC, SC?, TN?

6/13/2000 This mesic, basophilic, oak-dominated forest association occurs on soils derived from limestones or other basic substrates, on upper to mid slopUS AL, GA, KY, TN

1/31/2007 This vegetation has a naturally restricted range of distribution, being limited to The Barrens of the southeastern Highland Rim of Tennessee. MoUS TN

2/6/2001 This type is restricted to very scattered and small sites in the Piedmont of North Carolina. The occurrence of a number of species which are assUS NC, VA? 

8/11/2004 This type occurs in areas of mafic lithology in the Piedmont of North Carolina, southern Virginia, Georgia, and South Carolina. Only a small percUS GA, NC, SC, VA

2/7/2001 This type is restricted to very scattered and small sites in the Piedmont of North Carolina and South Carolina. The edaphic situation in which it oUS GA?, NC, SC?

10/24/2002 As currently known, this type is restricted to eastern Texas. More information is needed to determine whether or not it is found in Arkansas and/oUS AR?, LA?, TX

5/6/1999 This community occurs on only a small number of mountain summits in western Arkansas and eastern Oklahoma, on the Ouachita and Ozark nUS AR, OK

6/20/1997 This woodland association has a canopy dominated by <i>Quercus stellata, Quercus muehlenbergii</i>, and <i>Quercus marilandica</i>. PresuUS AL, MS

3/13/2001 US AR, OK

12/31/1997 This oak woodland is restricted to the Inner Nashville Basin of Tennessee, where it occurs in association with Limestone Cedar Glades, in deepUS TN

9/5/2008 This woodland association is found in a restricted range and specific set of habitat conditions. It is known from areas of exposed, droughty soils US AL?, KY, TN

12/21/1999 As described, this association is naturally restricted to barrier islands and inland beach ridges along the upper Texas coast. These forests are hUS TX

1/24/2000 This association is naturally very restricted in range and environmental setting. It is found only on shell middens located within a matrix of marsh US AL, FL, LA, MS, TX?

12/31/1997 This maritime forest association has a low to moderately high tree canopy, often stunted and pruned by salt spray into streamlined shapes. This US AL, FL, GA, MS?, NC, SC

12/15/1994 This community has a naturally limited distribution, occurring only within a small area on the Gulf Coast of Texas (Upper Coastal Prairie), on uplUS TX

12/10/1999 This forest is only found on ancient beach ridges that run parallel to the coast in the Chenier Plain of Louisiana and possibly Texas. Because theUS LA, TX?

12/20/1999 This maritime hammock association has a restricted range, and the majority of this community has been lost or severely damaged by human deUS FL

10/20/1996 This association is naturally restricted in range and in the environmental context in which it occurs, being found only on coastal mainland areas US GA, NC, SC

10/9/1997 This maritime forest association is a low- to moderate-stature, broad-leaved evergreen forest of Virginia and the Carolinas that is often, though nUS GA?, NC, SC, VA

12/4/1999 This association is apparently restricted to natural levees of the ancient Mississippi River alluvial floodplain system in the coastal plain of LouisiaUS LA

2/2/2001 As currently described, this association is limited to the historic and current floodplains of the Brazos, San Bernard and Colorado rivers and their US TX

12/4/1999 Apparently restricted to natural levees in the ancient Mississippi River alluvial floodplain system in the coastal plain of Louisiana, this community US LA

1/3/2001 As currently described, this association is limited to the historic and current floodplains of the Brazos, San Bernard and Colorado rivers in the GuUS TX

2/19/2004 This xeric hammock community occurs in scattered locations along the Outer Coastal Plain of the South Atlantic and East Gulf Coastal Plain. ThUS AL, FL, GA, SC

8/14/1997 US FL
12/1/1997 US FL

10/2/1998 Though never widespread, this community once extended 129 km inland from the mouth of the Rio Grande and south along the Mexican coast MX, US MXTM, TX

1/31/2001 This community appears to be rare and restricted, but is poorly understood and circumscribed. As defined, its occurrence is limited to barrier islaUS FL?, GA, SC

5/20/2002 This association is restricted to temperate Florida and adjacent Georgia. Species richness in hydric hammocks is generally favored by the abseUS FL, GA

8/15/1997 US FL

12/1/1997 US FL

8/15/1997 US FL

1/30/2001 This community is apparently very rare, but additional information is needed to solidify its taxonomy and circumscription. This additional informaUS NC, SC?

10/20/1996 US TX

10/25/1997 This community occurs as isolated pockets in mesic desert canyons and along rocky floodplains of small, intermittent streams and is often assoMX?, US NM?, TX

1/2/1998 US AL, FL

12/1/1997 US FL

12/1/1997 US FL

1/8/2007 This community is restricted to Carolina bays and swales (e.g., in the Francis Marion National Forest, South Carolina), which have had a frequeUS GA?, SC

12/1/1997 US FL

1/30/2001 This community type is restricted to small, clay-based Carolina bays in the middle and inner Coastal Plain of North Carolina and South CarolinaUS NC, SC

1/23/2000 This community occurs in seasonally flooded Carolina bays and other isolated depressions (surrounded by uplands). Historically, occurrences oUS GA?, NC, SC

12/1/1997 US FL

12/1/1997 US FL

1/31/2001 This community type appears to be rare, occurring only in highly acid, seasonally flooded depressions in North Carolina and South Carolina. SuUS NC, SC

6/23/1997 US AL?, FL, MS?

5/20/2002 US FL, GA?

6/23/1997 US FL

6/23/1997 US NC, VA

12/15/1994 This community is restricted to Texas, with a few known occurrences in the southern and eastern portion of the Edwards Plateau in central TexaUS TX

12/28/2000 This community needs further assessment to determine validity, composition, rarity, and distribution. Grank was changed from G2? to G2Q to inUS AR, OK

6/25/1997 US MD, NC?, VA

9/13/1997 US FL

1/30/2001 This community is apparently restricted to freshwater portions of major rivers on the Outer Coastal Plain of North Carolina and perhaps South CUS NC, SC?, VA?

9/4/2002 This community is uncommon within a small area of the East and Upper East Gulf coastal plains. Stands are impacted by the removal of commUS AL, GA

12/14/1998 This Southern Blue Ridge/upper Piedmont cove forest is naturally uncommon because of its limitation to mafic substrates. It is threatened by logUS GA, NC, SC, TN?

12/14/1998 This community is somewhat more common and secure than herbaceous and shrub-dominated nonalluvial wetlands of the Southern Blue RidgeUS GA, KY, NC, PA, SC, TN, VA

9/21/2001 This type appears to be quite rare naturally because of its small patch size, its apparent geographic restriction, and the paucity of suitable, high-US MD, PA?, VA, WV

9/29/2004 This community is uncommon and geographically restricted to the Great Smoky Mountains, Tennessee, and to Joyce Kilmer W US NC, TN ilderness in wes

12/31/1997 <i>Tsuga caroliniana</i> communities, in general, have a restricted range, occurring only in the southern Blue Ridge and upper Piedmont and aUS NC, TN 

12/31/1997 <i>Tsuga caroliniana</i> communities, in general, have a restricted range, occurring primarily in the Southern Blue Ridge, with scattered occurrUS NC, SC, TN?, VA

12/11/1998 The global range of this association has yet to be clearly delimited. It is a conspicuous part of forest vegetation in the Columbia Bottomlands areUS LA?, TX 

10/5/1999 This is probably a naturally uncommon community because <i>Abies concolor</i> is at the upper elevational limits of its distribution while <i>AbUS OR

10/14/1997 A naturally very restricted range of distribution of <i>Chamaecyparis lawsoniana</i> has been compounded by impacts from logging and introduUS CA, OR

10/14/1997 A naturally very restricted range of distribution of <i>Chamaecyparis lawsoniana</i> has been compounded by impacts from logging (as a result US CA?, OR

10/21/1997 While the remaining stands are fairly stable and not very threatened, this is a very rare association. It is restricted to northern slopes on generallUS CA, OR 

11/30/1999 This association is a very rare association that is restricted to the Klamath-Siskiyou region. Most stands tend to be small, and many are threatenUS CA?, OR

3/29/1999 <i>Picea breweriana</i> is endemic to the Klamath-Siskiyou region. Furthermore, it rarely codominates forest stands, making this a rare commuUS CA?, OR

4/7/1998 This type shows very restricted range of occurrence and few high-quality stands. There are approximately existing 10 element occurrences for tUS CO, NM?

11/9/2000 This association is only known from the Warner Mountains of south-central Oregon and northeastern California, where it is a local, fairly rare coUS CA, OR

2/1/1996 This is a forested association restricted to a fairly local area in south-central Oregon, and perhaps adjacent northern California. It occurs within a US CA?, OR

12/10/1999 This minor association has been described from the mountains of Colorado and may also occur in New Mexico and Arizona. Less than 20 occuUS AZ?, CO, NM

11/13/1997 This plant association is known only from the higher elevations of the Pinaleno and Santa Catalina mountains, below the elevational zone where US AZ

12/1/2000 This montane riparian association is restricted to small, scattered sites along stream channels throughout its range where plants, particularly treMX?, US AZ, NM

10/20/1999 This is a very rare community, found on the eastern slopes of the Mt. Hood National Forest, Oregon, where low elevation western Oregon flora hUS CA, OR

12/15/1998 This is a productive, valuable, late- to mid-seral forest plant association which is largely unprotected. Because of an unusual climate, it is found US OR, WA

10/22/1997 This is an association which has likely always been very rare. It is a diverse, productive, old-growth forest which occurs along streams in cool arUS OR
11/30/1998 This association is primarily found in and along the margins of the W US OR, WAillamette Valley, extends north to Olympia, and occasionally can be found in 

11/30/1998 This community has a restricted natural range to the eastern Cascades of W US OR, WA ashington and perhaps in Oregon. This is a mid- to late-seral wood

10/24/1997 This plant association occurs as few, isolated stands over a relatively narrow geographical range located in north-central Idaho, and in northeasUS ID, OR 

11/30/1998 This community has a relatively narrow range in the eastern Cascades of W US OR, WA ashington and Oregon. This is a mid- to late-seral forest community 

1/31/2007 This regionally endemic forest association occurs within the maritime-influenced climatic region of the northern Rocky Mountains of northeastern US ID, MT?, OR, WA?

4/20/2000 This community has a restricted natural range to north-central Idaho with outliers in adjacent Montana, Oregon, and W US ID, MT, OR, WA ashington. This is a late-s

11/30/1998 This association occurs in relatively few isolated, evenly distributed stands over a relatively restricted range of western Idaho, and possibly the OUS ID, WA? 

12/17/2000 This is a regional endemic association restricted to a narrow climatically defined area in the southeastern Cascade Mountains of W US WA ashington. It 

11/14/2000 This association occupies a small acreage in a very limited geographic and environmental range, i.e., dry sites at high elevations in the extreme US WA

11/13/1997 This plant association is known only from a few high-elevation sites in the Pinaleno Mountains of Arizona. Catastrophic events such as spruce bUS AZ

10/17/2002 This association has an estimated 50-100 occurrences covering probably somewhere around 1000 acres. It is limited to portions of the Puget LoCA, US BC, OR, WA

11/7/1997 This association is a narrow regional endemic which is undergoing continued fragmentation and degradation throughout its range due to agricultUS CO

11/30/1998 This is a minor type that is known from the Overthrust Mountains of northeastern Utah, northwestern Colorado and possibly Idaho and W US CO, ID?, UT, WY? yoming

2/1/1996 US ID

11/30/1998 This plant association is a regional endemic of the deeply incised Snake River canyonlands in western Idaho. It occurs within a relatively discretUS ID

9/21/2000 This regionally endemic plant association is known from the western region of the Blue Mountains ecoregional section, in Idaho, Oregon and W US CA?, CO, ID, OR, WA a

11/4/1997 This naturally rare, regionally endemic plant association is known from one location in the Owyhee Uplands ecoregional section, in Oregon. It's oUS ID, OR

11/30/1998 This is a regionally endemic plant association of the Owyhee Uplands, southern Challis Volcanics, and western portions of the Northwest Basin US ID, NV?, OR

10/21/1997 As with other <i>Chamaecyparis lawsoniana</i> associations, the very restricted range of distribution of <i>Chamaecyparis lawsoniana</i> and US CA, OR

10/21/2002 This association is restricted to riparian streams and wetlands in serpentine soils of southwestern Oregon and northwestern California, as well aUS CA, OR

11/13/1997 This association is restricted to cool and moist slopes and drainages with northern or eastern aspects, elevations 1460-1770 m in the Dragoon, US AZ

12/15/1998 The distribution of this woodland association includes W MX?, USood Canyon near Clifton, in the vicinity of Sedona and local elsewhere in southern and sAZ, NM

1/27/2000 Scattered distribution within its range. Although over 30 stands are known, many of them are small, and all are threatened by fire suppression. TUS CA, OR

1/27/2000 Scattered distribution within its range. Although over 30 groves are known, many of them are small, and all are threatened by fire suppression. TUS CA

10/1/2002 US OR, WA?

10/1/2002 US OR

9/28/2004 This association requires low-gradient floodplain habitats in which natural hydrological processes are operational to ensure reproduction and maMX?, US AZ?, NM

11/30/1998 This is a very rare association restricted to exposed ash soils. There are only a few occurrences, and these are threatened by mining, grazing, aUS CA?, NV?, OR

11/30/1998 The range of this association is in the Owyhee Uplands and Basin and Range sections in Oregon and Idaho, and probably in extreme northern NUS ID, NV?, OR

2/15/2006 The range in rank reflects the limited area in which this vegetation type may occur and uncertainty about its status. It appears to be uncommon US CO, UT, WY

12/15/1998 This woodland community is widespread north of the Mogollon Rim, but has been heavily modified by the impacts of grazing and altered fire regUS NM

11/14/1997 This association has been described from only one plot on the lower, southern slopes of the Pryor Mountains, but noted elsewhere in the vicinity US MT 

11/7/1997 This woodland is regionally endemic, occurring on granitic outcrops and on Fountain Formation exposures in the Front Range of north-central CUS CO, MT?, WY? 

11/30/1998 Distribution of this association is restricted to the eastern slopes of the northern Colorado Front Range in the Roosevelt National Forest. Few ocUS CO, WY?

12/29/2000 A relictual woodland community limited to specific and limited environmental conditions that have been altered by cattle grazing, fire suppressionUS CO, WY? 

1/14/2004 CA, US AB, ID?, MT, WA

11/30/1998 This community appears to be widely distributed but in isolated patches. It is located in the high elevations of the eastern Cascades in northern CA?, US AB?, ID?, MT?, WA 

12/1/1997 US HI

12/15/1998 Across the range of the type, stands are typically small (less than one acre) and readily accessed and degraded by livestock (and wild ungulate) US ID, MT, WY? 

10/14/1997 This association, the wettest within the <i>Picea engelmannii</i> Series, has a naturally restricted, perhaps relictual, distribution. It occurs on peUS MT 

12/15/1998 This community type is naturally uncommon but found locally in high-elevation forests of the Sacramento Mountains and Chiricahua Mountains US AZ, NM

10/9/1997 The G2 rank is based on a relatively limited geographic range (central and eastern Idaho and western W US ID, MT?, OR, WY yoming); on a sporadic occurrence in m

12/12/1999 These late-seral forests are found in relatively mesic, easily accessible sites. They produce large volumes of timber and are often disturbed by loUS AZ, NM

11/14/1997 This association has only been documented from a small area of the Front Range of the southern Rocky Mountains west of Denver. It occupies US CO

12/30/2000 This riparian conifer woodland is known only from Colorado and southern Utah, though it may occur in northern New Mexico. Stands are threateUS CO, NM?, UT

2/23/1994 US UT, WY

2/23/1994 This association has a restricted range of occurrence on the western slope of the Colorado Rocky Mountains. Many stands have been eliminateUS CO

5/1/2000 This community is known from the coast of northern California, Oregon, W US CA, OR, WA ashington and southern British Columbia, where stands are restricted 

10/21/2002 About 20 stands of this association are known to exist in Oregon and W US OR, WA ashington, covering some 5000 acres. About 85% of this association is t

12/1/2000 This plant association is ranked G2G3 because it is relatively uncommon yet widespread on peatlands of south-central and southeastern AlaskaUS AK

4/10/1999 This moderately widespread association occurs in relatively few, unevenly distributed, isolated stands within the northwestern portion of the YellUS ID, MT, OR, WY

11/27/2000 This forest association has a very limited range in Oregon where it is found on Fremont National Forest. This type occurs in small patches, usuaUS CA?, OR
11/30/1998 This community is widely distributed but restricted to the high elevations of the eastern Cascades in northern W US WA ashington and probably southern 

11/7/1997 There are ten recorded locations for this association in the southern Rockies of Colorado. This type is a regional endemic with only a few recordUS CO

11/17/1999 These woodlands occur on valley bottom and foothill terraces and are fire maintained communities. <i>Pinus attenuata</i> trees have closed coUS CA, OR 

10/28/2002 CA?, US BC?, WA

12/1/2000 This local association is restricted to sand dunes along the Pacific coast between northern California and southwestern W US CA?, OR, WA? ashington, with most r

10/20/1997 This association is limited and patchy in its distribution to the "Borderlands" of southwestern New Mexico, and possibly southeastern Arizona anMX?, US AZ, MXCH?, NM, TX?

10/21/1997 This association is limited in its distribution to the "Borderlands" of southwestern New Mexico, and possibly southeastern Arizona and the Trans-MX?, US AZ, MXCH?, NM

10/20/1997 This association is restricted to the "Borderlands" of southeastern Arizona and southwestern New Mexico, and possibly very northern Sierra MaMX?, US AZ, MXCH?, NM

11/14/1997 This is a rare, regionally endemic association. It is poorly known, with only five documented locations from four counties (Montrose, San Miguel, US CO, UT

12/15/1998 This woodland association occurs locally in the landscape in central and northern New Mexico. As a "decreaser", <i>Andropogon hallii</i> is an US NM

12/15/1998 This savanna woodland is presently known from the Sacramento and Guadalupe mountains of south-central New Mexico. There is little documeUS NM

10/21/1997 This association is limited in its distribution to the "Borderlands" of southeastern Arizona and southwestern New Mexico and the northern Sierra MX?, US AZ, MXCH?, NM

10/21/2002 This is a very local plant community, currently restricted to coastal-influenced, serpentine areas in southwestern Oregon and adjacent CaliforniaUS CA, OR

3/6/2003 This association is only known from Point Reyes National Seashore, and is confined to a very small area. US CA

11/30/1998 This association was never very common, being restricted to high-elevation riparian zones in south-central Oregon. Many areas have been loggUS OR

11/30/1998 This association is restricted to hot, dry, high-elevation sites, with low moisture-holding capacity soils, in the Oregon Cascades. These abiotic reUS CA?, OR

12/17/2000 This association is restricted to a limited area on the W CA?, US enatchee National Forest in W BC?, WA ashington. This association is a small- to large-patch wood

10/23/1997 This association is very local, with all known sites located within the area between Badger Creek and Jordan Creek, on the southeastern side of US OR

11/30/1998 This community has a narrow range in the eastern Cascade foothills of W US WA ashington and perhaps adjacent Oregon. The number of occurrences 

1/27/2000 This woodland association currently found in a narrow area in the East Cascades near the Columbia River Gorge and north into the Yakima IndUS CA?, OR, WA 

2/1/1996 US MT

12/30/2000 This association is known only from the Front Range of Colorado. Stands occur along foothill and montane streambanks on the southern aspectUS AZ?, CO, NM?

2/1/1996 This woodland association has been rudimentarily documented (Roberts 1980) to occur only in the Bear's Paw Mountains (wholly within the RocUS MT

1/3/2000 The total range of this association is limited to a few hundred square miles. Logging, land conversion and mining have reduced the extent of this US CA?, OR

3/29/1999 Historical fires were typically less frequent in this type than most other <i>Pinus ponderosa</i> communities, and thus the threat of fire suppressUS CO?, ID?, NM, OR

11/30/1998 This association is restricted to southern Oregon east of the Cascades. It is restricted to relatively high-elevation sites with soils rich in pumice. TUS OR

3/29/1999 This fire-dependent rare community is restricted to areas in central Oregon and adjacent W US ID, OR, WA ashington and Idaho, which are moist enough to sup

11/30/1998 This association is restricted to mid-elevation sites in northeastern Oregon. The abiotic requirements are broad enough that it is likely that this aUS OR

11/13/1997 This semi-riparian woodland is restricted to terraces along perennial streams and large washes south of the Mogollon Rim in Arizona, between US AZ

11/4/1997 This relatively widespread plant association of the Idaho Batholith, Bitterroot Mountains, and Palouse Prairie ecoregional sections occurs as dispCA?, US BC?, ID, MT, WA

10/24/1997 This is an association which was formerly widespread in a narrow range, along plateaus and benches between 3000 and 5600 feet in the PumicUS CA, OR

11/22/2000 This is a local community, restricted to the pumice zone of central Oregon. It has a limited distribution with less than 20 occurrences estimated. US CA?, OR 

11/22/2000 Although it is regionally endemic, this community is currently less threatened than other Ponderosa pine communities, with an estimated 20-50 oUS OR

3/29/1999 This type is both very rare and very threatened. This association occurs on the Bly and Lakeview Ranger Districts of the Fremont National ForesUS CA?, OR 

12/1/2000 This lowland riparian association is restricted to scattered stands along the Gila River and Animas Creek in New Mexico, but potentially could ocUS AZ?, NM

10/21/1997 Few intact examples of this association remain in the southwestern U.S. The association continues to be in decline, primarily as a function of hyMX?, US AZ, NM

9/27/2004 This association requires low-gradient floodplain habitats in which natural hydrological processes are operational to ensure reproduction and maMX?, US AZ?, NM

4/7/1998 US CO, NM, UT, WY

11/30/1998 ~<i>Populus angustifolia / Acer grandidentatum</i> Forest (CEGL000646)$$ is a minor type that is known from northeastern Utah and southeasUS ID, UT

11/30/1998 The range of this association apparently extends from central Colorado, north to north-central W US CO, NM, WY yoming, a distance of ca. 400 miles. So far, the 

12/27/1999 This riparian woodland association is rare and has only been described from 5 stands in three mountain ranges in Utah. There are over 20 occuUS CO, NV, UT, WY

12/30/2000 This newly described riparian woodland is known from only one location in the Sangre de Cristo Range of southern Colorado, but is suspected tUS CO

10/22/2002 This association is a relatively wide-ranging and broadly defined association occurring on infrequently flooded alluvial terraces of low-elevation sCA?, US BC?, ID, MT?, OR, WA, WY

2/23/2004 This association has a restricted range of occurrence on the eastern slope of the northern Rockies, with an unusual combination of tree dominaCA, US AB, MT

10/17/2002 There are relatively few occurrences, probably less than 100, remaining of this association, of which only a small percentage are highly viable. TCA?, US BC?, OR, WA

2/1/1996 US WA

10/17/2002 There are very few to few occurrences of this association and a limited areal extent. It appears to be limited to a small geographic range, the weUS OR?, WA

10/17/2002 This minor riparian forest occurs only in the Kettle and Selkirk ranges of northeast W CA?, US BC?, WA ashington and probably adjacent British Columbia. It is rare 

9/28/2004 This major association of the Rio Grande and Pecos basins has undergone significant declines as a result of impoundments and subsequent rivUS AZ?, NM, UT?

9/28/2004 This association has likely undergone significant declines in the San Juan River basin as a result of impoundments and subsequent river regulatUS AZ?, NM, UT

11/4/1997 This association occurs along low-elevation rivers in a semi-arid region where agricultural activities and hydrologic modifications have had great US CO, NE?, NM?, UT, WY? 

7/21/2004 This major association of the Rio Grande and San Juan River basins has undergone significant declines as a result of impoundments and subseUS AZ?, CO, NM, UT?
9/28/2004 This associations has undergone significant declines in the Rio Grande and Pecos basins as a result of impoundments and subsequent river reg

US AZ?, NM, UT?

12/22/2000 This riparian woodland association is documented only in 3 areas in the lower South Platte River in northeastern Colorado, though thought to ocUS CO, WY?

12/19/2000 This riparian forest association is ranked G2G3 because it has a relatively restricted range, narrow ecological amplitude, and is highly susceptibCA, US AB, MT, SK

9/28/2004 This association has likely undergone significant declines in the Canadian River and Pecos basins as a result of impoundments and subsequent US CO?, NM

9/28/2004 This association has likely undergone significant declines in the Rio Grande and Pecos basins as a result of impoundments and subsequent riveMX?, US AZ?, NM, UT?

9/28/2004 This association may be a highly restricted local endemic community. W US NM, TX? hile a significant portion of stands occurs within a national park, an equ

11/5/1997 This association has only been documented from river floodplains of the lower Colorado, Yampa, and San Miguel rivers in extreme western ColoUS CO, UT

9/28/2004 This association, like other montane riparian communities of the Southwest, has likely been impacted by livestock use and hydrological alteratioUS AZ?, NM 

9/28/2004 This association may be a highly restricted local endemic community. W US NM, TX? hile a significant portion of the stands is within a national park, an equa

12/1/2000 This lowland riparian association is limited to scattered stands in Arizona, New Mexico, and southwestern Utah where plants, particularly trees aMX?, US AZ, MXSO?, NM, TX?, UT

12/1/2000 This lowland riparian association is restricted to scattered stands along the Gila River in New Mexico where plants, particularly trees and shrubsUS AZ, NM

12/1/2000 This lowland riparian association is restricted to scattered stands along the Gila River in New Mexico where plants, particularly trees and shrubsUS AZ?, NM

4/4/2001 US AZ?, NM

2/23/1994 Few intact examples of this association remain in the southwestern United States. The association continues to be in decline, primarily as a funcMX?, US AZ, CA?, CO, MXCH?, MXSO?, NM, TX, UT

12/1/2000 This lowland riparian association is limited to southwestern New Mexico and southern Utah where plants, particularly trees and shrubs, have acUS AZ?, CA?, NM, NV?, UT

10/21/1997 Few intact examples of this association remain in the Southwest U.S. The association continues to be in decline, primarily as a function of major US CA, NM, UT

11/7/1997 Few intact examples of this association remain in the southwestern U.S. It has been documented on the Gray Ranch of the Animas Mountains iMX?, US AZ?, NM

12/14/2000 This association seems to be naturally rare, having been described from a small geographic range (the southern Salt River and W US WY yoming moun

9/27/2004 The G2G3 rank is based on the assumptions that this association occurs over a fairly wide geographic range, but that there are few occurrences US CO, NV, UT, WY

2/23/1994 US UT, WY

10/1/2002 CA, US BC, OR, WA

10/16/2002 This is an uncommon wetland forest association that is known from few occurrences in Oregon and W US CA?, NV?, OR, WA ashington, and is located in relatively rest

12/16/1999 This association is known from fewer than 30 stands in Colorado. The literature indicates that stands occur on very well-drained soils at the midUS CO, WY

11/30/1998 This association has been described only from the WUSyoming Range in western W WY yoming, where it is associated with moist or wet sites at 8400-

11/7/1997 This association is restricted in range of occurrence to a relatively small region of mountain ranges in the southeastern Rocky Mountains of ColoUS CO, UT 

11/30/1998 This association is known to occur from northeastern Utah north to west-central W US ID, MT, UT, WY yoming and northwestern Montana and west to southeastern 

2/23/1994 US CO, UT

12/1/1997 US HI

11/30/1998 This plant association has almost entirely disappeared as a result of rural residential development, secondary succession (from an altered fire reUS CA, OR, WA 

3/29/1999 Ancient redwoods are extremely rare throughout their native range. This redwood association is one of the most productive redwood communitieUS CA, OR

11/14/1997 Well protected in small remnants and on Redwood National Park, the remaining examples of this association currently occupy less than 10 percUS CA, OR

11/30/1998 This community has a very limited natural range, being restricted to the northern Puget Lowland of W US OR, WA ashington and adjacent Oregon, and the G

11/3/1997 This association is found exclusively in the central to northern Puget Lowland of W US WA ashington. Very few good quality occurrences remain becaus

10/23/2002 This is a rare and local association, but is common on large sand dunes along the Pacific coast between northern California and Tillamook Bay, US OR

11/3/1997 This community is naturally common in a limited area of the Puget Lowland but has been much reduced and degraded. Very few good-quality oUS WA

7/6/2005 The rank for this type needs to be reviewed. This association has now been described from the Bear's Paw Mountains of central Montana, as wUS CO, MT, WY

10/24/2002 This is a fairly rare, local association found only on the east side of Mount Hood. Historically the stands have been heavily impacted by livestock US OR

11/14/1997 This community was naturally common in a restricted geographic area in and around the San Juan Islands, and relatively rare in a larger area. IUS WA

2/1/1996 US MT

11/30/1998 This association has a naturally restricted distribution being found on very steep, well-drained terrain of mostly northern exposures at the upper CA?, US BC?, CO 

2/1/1996 This community has limited geographic distribution and habitat conditions on which it can occur. US MT

10/21/1997 This association is limited in its distribution to the "Borderlands" of southwestern New Mexico, southeastern Arizona and possibly in the Trans-PMX?, US AZ, MXCH?, NM, TX?

11/14/1997 This community has a restricted natural range (the rainshadow of the Olympic Mountains) and occurs in very specific environments. The total nuUS WA

3/29/1999 This is a local, rare, and entirely unprotected association. Most of the stands are fairly small, found on areas which are fairly flat. It has decreaseUS CA?, OR, WA

10/21/1997 This association is limited in its distribution to the "Borderlands" of southeastern Arizona and southwestern New Mexico, and possibly in the TraMX?, US AZ?, MXCH?, NM

11/16/2000 This forest association is restricted to the southern Puget Lowland of western W US OR, WA ashington, the Willamette Valley and the Umpqua Valley of wes

12/1/2000 This is still a fairly widespread vegetation type, with between 30 and 100 stands remaining. Unfortunately, no stands are known in good conditioUS CA, OR

2/1/1996 This association has a restricted range of distribution. Fire suppression has resulted in shifts in species composition and vegetation structure. US CA, OR

11/16/2000 This woodland association is only known from the Puget Lowland of western W CA?, US BC?, WA ashington and the Georgia Basin of southwestern British Columb

10/28/2002 US OR

11/30/1998 This community has a narrow natural range along the southeastern Cascade foothills in W CA?, US BC?, WA ashington and adjacent Oregon. The number and size 

11/30/1998 This plant association has almost entirely disappeared as a result of rural residential development, secondary succession (from an altered fire reUS CA, OR, WA 
1/20/2000 This woodland alliance was formerly extensive in the Sacramento and San Joaquin valleys, but high quality stands have been virtually eliminate

US CA

12/1/1997 This association has a very restricted range of distribution. It may have been more extensive in the past, prior to settlement and the introduction US CA

10/1/2002 US OR, WA

12/1/1997 US HI

10/13/1997 This community has been described from the central to southern portion of the W US OR est Slope Cascade ecoregion, and the northern end of the Kla

11/30/1998 This association is found only in the southern Oregon Cascades, being restricted to moist easterly slopes. Although this association is restricted US CA?, OR

11/30/1998 This is a regionally endemic plant association occurring in low-elevation, easily accessible sites, on moist low to moderate slopes on mid, lower, US ID

11/30/1998 This riparian community has a restricted natural range to portions of northeastern W CA?, US BC?, ID?, MT, WA ashington, northwestern Montana, and most probably adjac

10/16/1997 The only description of this community (Atzet and McCrimmon 1990) is from the central to southern portion of the W US OR, WA? est Slope Cascade ecoregio

1/29/2001 This regional endemic plant association is restricted to warm, moist, gentle north- to east-facing slopes within the Pacific maritime-influenced cliUS ID

11/4/1997 This naturally rare, regionally endemic plant association is known from the Selkirk Mountains of W US ID, WA ashington and Idaho. It is found in evenly disp

10/29/1999 This rare association is documented on two ranger districts and one BLM district in southwestern Oregon. <i>Quercus sadleriana</i>, a diagnosUS CA?, OR

11/30/1998 This community has a highly restricted natural range in northeastern W US WA ashington and adjacent British Columbia. It is apparently restricted to a s

2/1/1996 This association has only been described from a small area of the Olympic Mountains, on some of the driest and coldest sites capable of suppoUS ID?, WA 

11/4/1997 This regionally endemic plant association is restricted to seasonally saturated soil of high-elevation mountainous cirques of the western slope of US ID
TNC Ecoregions USFS Ecoregions

2:C, 3:C

69:C

2:C 242A:CC

2:C 242A:CC

2:C M242A:CC

1:C, 3:C

62:C 232Ab:CCC

61:C 221Db:CCC

62:C 232Aa:CCC

59:C M212Ba:CCC

62:C 232Aa:CCC, 232Ab:CCC, 232Ac:CCC

57:?, 58:C, 62:C 232Ac:CCC, 232B:CC, 232C:C?

59:C M221Aa:CCC

59:C M221Aa:CCC, M221Ba:CCC

59:C, 63:C M221Ba:CCC, M221C:CC

60:C 212Fd:CCC, 221Bd:CCC

62:C 232Ab:CCC

48:C, 64:C 212E:PP, M221C:CC

58:C 232Ac:CCP, 232Bt:CCC, 232Bz:CCC, 232Ch:CCC

58:C, 62:C 232Ab:CCP, 232Bz:CCC, 232Ch:CCC

59:P, 61:C 221Db:CCC, 231Al:???, M221Da:PPP

57:C, 58:C 232Br:CCC, 232Ch:CCC, 232Cj:CCC

25:C M334A:CC

48:C, 64:C 212Hw:CCC, 222Jj:CCC, 222Qa:CCC

33:C, 36:C, 37:C 251Cg:CCC, 251Cq:CCC, 251Ea:CCC, 251Fa:CCC

36:C 251Cc:CCC, 251Cd:CC?, 251Cj:CCC

36:C, 46:C 212Jm:???, 222Kh:CCC, 251:C

37:C 251:C

25:C, 26:C 331F:CC, M334A:CC

43:C, 44:C 222Ca:CCC, 222Di:CPP

40:C, 41:C, 53:C 232Bj:CCC, 232Fa:CCP, 232Fb:CCP, 232Fe:CCC

51:C M221Dc:CCC, M221Dd:CCC

51:C M221Dc:CCC, M221Dd:CCC

43:C 231Ba:CCC, 231Bk:CCC

29:C 255Ai:CCC, 315D:CC

21:C, 24:C 321A:CC

51:C M221Dc:CCC, M221Dd:CCC

54:C 411Aa:CCC, 411Ab:CCC

24:C 321A:CC

54:C 411Af:CCC

56:?, 57:C 232Cb:CCC

54:C 411Ag:CCC

56:P, 57:C 232Cb:CCC, 232Ce:CCP

30:C 315E:CC

54:C 411Ae:CCC

54:C 411Ag:CCC

54:C 411Ag:CCC

57:C 232Ci:CCC

30:C, 31:C 315E:CC

43:C, 53:C 232Bd:CCC, 232Bi:CCC, 232Bs:CCC

43:C, 53:C 231Bh:CCC, 232Ba:CCC, 232Bd:CCC, 234Ad:PPP
51:C M221A:C?, M221B:C?, M221C:C?, M221Dc:CCC, M221Dd:CCC

51:C M221A:C?, M221B:C?, M221C:C?, M221Dc:CCC, M221Dd:CCC

54:C, 55:C 232Gb:CCC, 411Ad:CCC, 411Ag:CCC

54:C, 55:P 232De:CPP, 411Ae:CCC, 411Af:CCC

57:C 232Cb:CCC

44:C 222Fa:CCC, 222Fb:CCC

44:C 221Hc:XXX, 222Fa:CCC, 222Fb:CCC, 222Fc:CCC, 222Fd:CCC

57:C 232Ci:CCC

57:C 232Ch:CCC

40:C, 41:P 231Eh:CCC

54:C 411Ab:CCC

54:C 411Ab:CCC

54:C 411Ag:CCC

38:C, 43:?, 44:C, 50:? 222A:CC, 222Eb:CCC

53:C 232B:CC

52:C 231Af:CCC

50:C 221H:PP, 221J:PP, 231C:CC, 231D:CC

57:C 232Ci:CCC

51:C M221Dc:CCC, M221Dd:CCC

51:C M221Dc:CCC, M221Dd:CCC

51:C M221Dc:CCC, M221Dd:CCC

53:C 232Dc:CCC

55:C 232Bf:CCC

53:C 232Dc:CCC

55:C 232Bf:CCC

43:C, 53:? 231Bb:CCC, 231Bd:CCC, 231Be:CCC, 231Bg:CCC

40:C, 41:C 231Ea:CCC, 231Ef:CCC, 231Eh:CCC, 232Fe:CCC

52:C 231A:CC

38:C, 39:C 222:?, 231:?, M222:?, M231:C

54:C 411Ag:CCC

54:C, 55:P 232Da:PPP, 411Af:CCC

54:C 411Ac:CCC

53:C 232Dc:CCC

53:C 232Bj:CCC

56:P, 57:C 232Bs:CCC, 232Cb:CCC

40:C, 41:C 231Ea:CCC, 232Fa:CCC, 232Fb:CCP, 232Fe:CCP

56:?, 57:C 232Cb:CCC

52:C 231Aa:CCC

53:C, 56:C 232Br:CCC

56:C 232Ca:CCC

56:C, 57:C 232Cb:CCC, 232Ce:CCC

56:C, 57:C 232C:CC

57:C 232Cb:CCC

57:C 232:C

57:C 232:C

52:C, 57:? 231Ao:CCC, 232:?

57:C 232Bv:CCP

56:P, 57:C 232Cb:CCC, 232Ce:CCC

56:P, 57:C 232Cb:CCC, 232Ce:CCC

53:C 232Bg:CCC, 232Bj:CCC

41:C 232Fa:CCP, 232Fb:CCC

53:C 232Ba:CCC
55:C, 56:C 232Bf:CCC, 232Br:CCC

57:C 232B:C?

56:C, 57:C 232Bq:CCC

41:C 232Fa:CCC

41:C 232Fa:CCC

56:P, 57:C 232Cb:CCC

41:C 232Fb:CCC

57:C 232Bq:CCC

51:C M221Dd:CCC

51:C M221Db:CCC

57:C 232Ch:CCC

51:C M221Dc:CCC, M221Dd:CCC

42:C

52:C 231Ae:CCC

42:C, 43:?

52:C 231Ae:CCC

39:C M231Aa:CCC

51:C M221Dd:CCC

44:C 222Fa:CCC, 222Fb:CCC

56:?, 57:C 232Ce:CC?, 232Ci:CCC

54:C 411Af:CCC

44:C 222Eb:CCC

50:C 231Dc:CCC

44:C 222Eb:CCC

51:C M221Aa:CPP, M221Dc:CCC

40:C 231Eb:CCC

40:?, 41:C 232Fa:CCC

40:C, 41:C, 43:C 231Bd:CPP, 231Ea:CCP, 231Ej:CCC, 232Fa:CCC

41:C 232F:CC

41:C 232Fa:CCC

52:C 231Ao:CCC

52:C 231Ae:CCC

41:C 232:C

42:C, 43:?

40:C 231Eb:CCC, 231Eh:CCC, 231Ej:CCP, 232Fb:CCC

31:C 231Fb:CCC, 232Eb:CCC

57:C 232Ch:CCC, 232Ci:CCP

56:C 232Cb:CCC, 232Ce:CCC

56:C 232Cb:CCC, 232Ce:CCC

54:C 411Ab:CCC

54:C 411Af:CCC

54:C, 55:C 232De:CCC, 232Gb:CCC, 411Ae:CCC, 411Af:CCP

54:C, 55:C 232Da:CCC, 232Gb:CCC, 411Ac:CCP, 411Af:CCC

54:C 411Ab:CCC, 411Ad:CCC

54:C 411Ae:CCC

53:C 232Dc:CCC

53:C 232Dc:CCC

57:C 232Ch:CCC

57:C 232Cb:CCC

57:C, 58:? 232Ch:CCC

57:C 232Ch:CCC

54:C 411Ae:CCC
44:?, 50:C, 51:C, 59:C M221Aa:CC?, M221Ab:CCC, M221Dc:CCC

50:C, 59:C M221Aa:CCC, M221Da:CCC

50:C 231Ca:CCC, 231Cd:CCC

51:C, 52:C 231Aa:CCC, M221Db:CCP, M221Dc:CCC, M221Dd:CCC

40:C 231Eb:CCC

5:C M261A:CC

1:C, 5:C M261A:CC

4:C M242C:CC

4:C M242C:CC

21:C M313A:CC

1:C M242:C

65:C M423:C

65:C M423:C

65:C M423:C

65:C M423:C

65:C M423A:CC

10:C, 18:C, 19:C 341B:CC, 342G:CC, M331E:CC, M341B:CC

6:C, 8:C 331A:CC, 342C:CC, 342H:CC, 342I:C?, M332A:CC, M332G:CC

6:C, 8:C 331A:CC, 342C:CC, 342H:C?, M332A:CC, M332G:CC

6:C, 8:C 342C:CC, M332G:CC

6:C, 8:C 342C:CC, 342H:C?, M332A:CC, M332G:CC

6:C, 8:C 342C:C?, 342H:CC, 342I:CC, M332G:CC

M332G:CC

4:C, 7:C, 8:C, 81:C M332A:CC, M332G:CC

4:C, 8:C, 81:C M332A:CC, M332G:CC

6:C, 8:C 331A:CC, M332G:CC

8:C M332F:CC

1:C M242A:CC

1:C, 5:C M242A:CC, M261A:CC

1:C, 5:? M242A:CC, M261A:??

1:C, 5:C M242A:CC, M261A:CC

5:C, 14:C M261A:CC

1:C, 5:C M242A:CC, M261A:CC

65:C M423A:CC

65:C M423A:CC

65:C M423A:CC

2:C 242A:CC

65:C M423A:CC

65:C M423A:CC

1:C, 14:C 263A:CC, M242A:CC

69:C M245C:CC

1:C, 5:P M242A:CC

1:C, 5:C, 14:C 263A:CC, M242A:CC, M261A:CC

1:C, 5:C, 14:C 263A:CC, M242A:CC, M261A:CC

2:C 242A:CC

24:C 321A:CC

24:C 321A:CC

24:C 321A:CC

6:C 342D:CC

1:C, 3:C, 5:C, 81:C M242A:CC, M242B:CC, M261A:CC

2:C 242A:CC

5:C M261A:CC, M261D:CC
4:C, 5:C M261A:CC

4:C, 6:C M242C:CC

4:C M242C:CC

2:C 242A:CC

6:C 342I:CC

4:?, 6:C 342B:CC, M261G:??

9:C M331B:CC

15:C, 16:C 261A:CC, 261B:CC

4:C, 6:? 342B:CC, M261G:CC

65:C M423A:CC

19:C, 20:C 341B:CC, M331G:CC, M331H:CC

2:C 242A:CC

6:C, 10:C 331A:CC, 342A:CC, 342G:CC, 342I:CC

1:C, 2:C M242A:CC

4:C, 6:C, 8:C 342H:CC, M332A:CC, M332G:CC

6:C, 8:C 342B:CC, 342C:CC, 342H:CC, 342I:CC, M332G:CC

20:C M331F:CC, M331I:CC

8:C M332G:CC

65:C M423:C

65:C M423:C

65:C M423:C

65:C M423A:CC

65:C M423A:CC

65:C M423A:CC

65:C M423A:CC

2:C 242A:CC

2:C 242A:CC

4:C M242C:CC

2:C 242A:CC

22:C, 24:C 321A:CC

4:C M242C:CC

2:C, 4:C, 5:C, 6:C, 14:C 242A:CC, 342I:CC, M242C:CC, M261A:CC, M261B:CC

4:C, 6:C 342I:CC, M242C:CC

4:C, 6:C 342I:CC, M242C:CC

2:C 242A:CC

11:C 313:?, 341:?

65:C M423:C

65:C M423A:CC

2:C 242A:CC

2:C 242A:CC

2:C 242A:CC

1:C M242A:CC

4:C M242C:CC

69:C

1:C, 3:C, 69:C

1:C, 3:C, 69:C

2:C

3:C M242B:CC

144:C

2:C

2:C, 3:C M242A:CC, M242B:CC

1:C, 3:C, 69:C M242A:CC, M242B:CC
1:C, 2:C, 3:C 242A:CC, M242A:CC, M242B:CC

3:C M242B:CC

1:C M242A:CC

69:C

1:C, 69:C M242A:CC

1:C M242A:CC

3:C M242B:CC

69:C

59:C M221B:CC

59:C M221Ba:CCC, M221Bc:CCC

57:C, 58:C 232Br:CCC, 232Ch:CCC, 232Cj:CCC

61:C, 62:C 221Ac:CCC, 221Ae:CCC, 221Ag:CCC, 221Ba:CCC, 232Ab:CC?, 232Ac:CCC

62:C 232Ab:CCC

60:C, 61:C, 62:C 212Fc:CCC, 221Ac:CCC, 221Ad:CCC, 221Ae:CCP, 221Ai:CCC, 221Ak:CCC, 221Ba:CCC, 221Bd:CCC, 221Dc:CC

60:C, 61:C 212B:CC, 212Fc:CCC, 221Ae:CCC, 221Af:CCC, 221Bd:CCC, 221Dc:CCC

48:C, 61:C, 64:C 221Ae:CCC, 222I:CC

58:C, 62:C 221Aa:CC?, 221Ab:CCC, 232Aa:CCC, 232Ab:CC?, 232Ac:CCC, 232Bz:CCC

51:C, 59:C, 60:C 212Fb:CCC, 212Fd:CCC, 212G:CC, 221Bd:CCP, M212Ea:CCC, M221Aa:CCC, M221Ba:CCC, M221Bb:CCC, M22

59:C M221Ba:CCC, M221Bb:CCC

59:C 212Fb:PPP, 212Fc:PPP, 212Fd:PPP, M221Ba:CCC, M221Bb:CCC, M221Bc:CCC

59:C M221Ba:CCC, M221Bc:CCC

61:P, 62:C 232Aa:CCC, 232Ab:CCP

58:C 232Ad:CCC

62:C, 63:C 212Cb:CCC, 212Db:CCC, 212Dc:CCP, 221Ab:CCC, 221Bd:CCC, M212E:CP

58:C, 62:C 212Db:CCC, 221Ab:CCC, 221Ac:CCC, 221Ak:CCC, 232Aa:CCC, 232Ab:CCC, 232Ac:CC?

62:C 232Ab:CCC, 232Ac:CCC

62:C 232Aa:CCC, 232Ab:CCC

61:C, 62:C 221Aa:CC?, 221Ae:CCC, 221Af:CCC, 221Ah:CCC, 221Bb:CCC, 221Bc:CCC

61:C, 62:C 221Ah:CCP, 221Ai:CCC, 221Al:CCC, M212Bb:CCP, M212Bd:CCP

61:C 221Ai:CCP, 221Al:CCP, M212Bb:CCP, M212Bd:CCP

57:C, 58:C, 62:C 232Ac:CCC, 232Bx:CC?, 232Bz:CCC, 232Ci:CCC

52:C, 59:C, 61:C 221Db:CCC

61:C 221Ba:CCC

62:C 221Ab:CCC, 221Ac:CC?, 221Ad:CCC, 221Ak:CCC, 221D:CP, 232Aa:CCC, 232Ab:CCC, 232Ac:CCC

59:C M221Ab:CCC

52:C, 58:C, 61:C 221Db:CCC, 231Ae:CCC, 231Ak:CCC, 231Al:CCC, 232Br:CCC

25:C, 26:C, 34:C, 35:C 251Aa:CCC, 331:?, 332:?, M334A:CC

26:C 331E:CP, 331F:CC, 332A:PP

45:C 222Ha:CCC, 222Hb:CCC, 222Hf:CCC, 222If:CCC

36:C, 44:C, 45:C, 48:C, 49:C, 61:C 212Fa:PP?, 212Fb:PPP, 221Bc:CCC, 221Ef:CCC, 221Fa:CCC, 221Fb:CCC, 221Fc:CCC, 222De:CCC, 222Ga:CC

44:C, 45:C, 48:C, 49:C, 50:C 221Eg:CCC, 221Fa:CCC, 221Ha:CCC, 222Db:CCC, 222Dc:CCP, 222De:CCC, 222Df:CCP, 222Ei:CCP, 222Ek:CC

26:C 331E:CC, 331F:CC, 332A:P?, 332C:PP, 332D:P?

48:C 221F:PP, 222Ha:CCP, 222I:C?, 222Jb:CCC, 222Jg:CCC, 222Jh:CCC, 222Ji:CCC, 222Jj:CCC, 222Ke:CC?, 222Kf

25:C M334A:CC

25:C M334A:CC

48:C, 64:C 212Ee:CCC, 212H:CC

38:C, 39:C 222A:CC, 231Gb:CCC, M222A:CC

46:C 222Lc:CCC, 222Ld:CCC, 222Le:CCC, 222Lf:CCC

46:C 222Lc:CCC, 222Lf:CCC, 222Md:CCC

27:C, 28:C 315B:CC, 331B:C?, 331C:CC, 331H:CP

20:C, 25:C, 26:C, 27:C 331F:CC, 331G:CC, 331H:CC, M334A:CC

37:C, 38:C, 39:C, 44:C 222Ab:CC?, 222Ag:CCC, 222Aj:CCP, 222Am:CC?, 222An:CCC, 222Ao:CCP, 222Aq:CC?, 222De:CPP, 222Di:CP
48:C 222Ib:CCC, 222Ic:CCC, 222Ie:CCC

36:C 251Ca:CCP, 251Cb:CCP, 251Cd:CC?, 251Cp:CCC, 251Cq:CCP, 332E:PP

26:C, 34:C 331E:C?, 331F:CC

25:C M334A:CC

36:C, 37:C, 44:C 222De:PPP, 251Cq:CCC, 251Ea:CCC

39:C, 42:C, 43:C, 44:C 222Ao:CPP, 222Ch:CCC, 222Db:CCC, 222Dc:CCC, 222De:CC?, 222Di:CCC, 222E:CP, 222Ga:CCC, 222Gb:CCC

45:C, 46:C, 48:C, 49:C 221Fb:CCC, 222Ha:CCC, 222Hb:CCC, 222Ia:CCC, 222If:CCC, 222Jb:CCC, 222Jh:CCC, 222Ji:CCC, 222Jj:CCC, 2

36:C, 38:C, 43:?, 48:C 222Ab:CCC, 222Af:CCC, 222Aj:CCC, 222If:CCC, 222Jh:CCC, 222Ji:CCC, 222Jj:CCC, 222Ki:CCC, 251Cc:CCC, 2

38:P, 42:C, 44:C 222:P, 234Ab:CCC, 234Ac:CC?

38:C, 39:C, 43:P, 44:C 222Ab:CCC, 222Ac:CCC, 222Ag:CCC, 222Ak:CCC, 222Am:CCC, 222An:CCC, 222Aq:CCP, 222Ca:CPP, 222Ch:C

32:?, 38:C, 39:?, 42:C, 43:C, 44:C 222Ab:CCC, 222Ae:CC?, 222Af:CCP, 222Db:CCC, 222Dc:CCC, 222Ga:CCC, 222Gb:CCC, 222Gc:CCC, 222Ge:C

47:C, 48:C 212Hi:CCC, 212Hw:CCC, 212Ia:CCC, 212Ib:CCP, 212Ja:CCP, 212Jb:CCC, 212Jr:CCC, 212Lb:CCC, 212Lc:CCP, 

44:C, 45:C, 50:C, 51:C, 52:C, 59:C 222Ea:CCC, 222Eb:CCC, 222Ej:CCC, 222Fd:CCC, 222Ha:CCC, 222Hb:CCC, 222Hc:CCP, 231Ak:CCC, M221Aa:C

46:C 222Ka:CCC, 222Lb:CCC, 222Lc:CCC, 222Ld:CCC

40:C, 41:C 231:P, 232Fe:CCC

40:C, 41:C 231:P, 232Fe:CCC

56:C, 57:C 232Bq:CCC, 232Cb:CCP, 232Ch:CCP

38:C, 39:C 231Gb:CCC, M222Aa:CCC, M222Ab:CCC

29:C 315D:CC

24:C 321A:CC, M313B:CC

52:C 231Aa:CCP, 231Af:CCC

39:C 231Gb:CCC

43:C, 44:C 222Ca:CC?, 222Cb:CCC, 222Ce:CCC, 222Cg:CCC, 222Dc:CCP, 222Dg:CCP, 222Eg:C??, 222G:CC, 231Be:CCC

50:C 221Hc:CCC, 221He:CCC

52:C 231Ao:CCC

54:C 411:C, M411A:CC

21:C, 24:C 321A:CC, M313B:CC

50:?, 51:C M221C:CC, M221Dc:CCC, M221Dd:CCC

51:C, 59:C M221Aa:CCC, M221B:C?, M221C:C?, M221Dc:CCC, M221Dd:CCC

59:C M221Aa:CCC, M221Ba:CCC, M221Bd:CCC, M221Da:CCC

51:C 221A:CC, M221Dc:CCC

50:?, 51:C, 59:? M221Ce:C??, M221Db:CCC, M221Dc:CCC

56:C, 57:C 232Ca:CCC, 232Cb:CCC, 232Ce:CCC

53:C 232Bm:CCC

53:C, 56:C, 57:C 232Bq:CCC, 232Br:CCC, 232Bu:CC?, 232Cb:CCC

53:C 232Bg:CCC, 232Bh:CCC, 232Bj:CCC, 232Dc:CCC

55:C 232Bf:CCC

53:C 232Bg:CCC, 232Bh:CCP, 232Bj:CCP, 232Dc:CCC

53:C 232Bf:CCC, 232Bj:CCC, 232Dc:CCC

57:C 232Cb:CCC, 232Ch:CCC

54:C 411Ad:CCC

53:C, 56:C 232Bh:CCC, 232Bi:CCC, 232Bj:CCC, 232Ca:CCC

53:C 232Be:CC?, 232Bg:CCP, 232Bh:CC?, 232Bi:CCP, 232Bj:CCC, 232Cc:CP?

40:?, 41:C 231Fa:CCC, 232Fe:CCC

53:C 232Ba:CCC, 232Bj:CCP, 234Ad:CC?

56:C, 57:P 232Ca:CCC, 232Cc:CCC

43:?, 53:C 232Bl:CCC, 232Bm:CCC

53:C 232Bg:CCC

42:C, 43:C 222Cb:CCC, 222Cc:CCC, 231Bh:CCC, 234Ab:CCC

40:C, 41:C 231Ea:CCC, 231Eb:CCP, 231Ek:CCP, 232Fa:CCC, 232Fb:CCP, 232Fe:CCC, 234Aa:CCC

50:C, 52:C, 57:C 231Af:CCC, 231Cc:CCC, 232Br:CCC, 232C:CC

51:C, 52:C, 59:C, 61:? 231Ae:CCC, 231Ak:CCC, 231Al:CCC, 231Ap:CCP, M221Aa:CCC, M221Ab:CC?, M221Da:CCC, M221Db:CC?, M2
51:?, 52:C 231Aa:CCC, M221D:??

53:C, 55:P 232Bi:CCC

54:C 411Af:CCC

40:P, 41:C, 42:P 231Ea:PPP, 231Ej:PPP, 232Fe:CCC, 411Af:CCC

31:C 255Db:CCC

42:C 234Ah:CCC

57:C 232Bs:CCC

44:C 221Hc:CCC, 222Ei:CCP, 222Ej:CCC, 222En:CCC

55:C, 56:C 232Bf:CCC, 232Bq:CC?, 232Br:CCC, 232Bu:CCC

32:C 255Ad:CCC

38:C 222Ag:CCC, 222An:CCC

38:C 222Ab:CCC, 222Ag:CCC, 222An:CCC

55:C, 56:C, 57:C 232Ce:CCC, 232Gb:CCC

43:C 231Ba:CCC, 231Bk:CCC

44:C 222Fa:CC?, 222Fb:CCC

53:P, 56:C 232Cb:CCC, 232Ce:CCC

40:C 231Eb:CCC

53:C 232Ba:CCP, 232Bj:CCP

53:C 232Bg:CCC, 232Dc:CCC

54:C 411Ag:CCC

54:C 411Ag:CCC

56:C, 57:C 232Bs:CCC

57:C, 58:? 232Ch:CCC

41:C 232Fa:CCC

57:C 232Cb:CCC

43:C, 50:P 231Bc:CCC, 231Bg:CCC, 231Dd:CPP

53:C 232Dc:CCC

53:C 232Dc:CCC

53:C, 56:C 232Ca:CCC, 232Ce:CCC, 232Dc:CCC

53:C, 55:?, 56:C 232Bg:CCC, 232Ca:CCC, 232Cb:CCC

56:C 232Br:CCC, 232Cb:CCC

51:C, 59:C M221Aa:CCC, M221Ba:CCC, M221Bc:CCP, M221Dc:CCC, M221Dd:CCC

51:C M221A:CP, M221B:CP, M221Dc:CCC, M221Dd:CCC

51:C, 59:C M221Aa:CCC, M221Ba:CCC, M221Bb:CCP, M221Bc:CCC, M221Bd:CCP, M221Be:CCP, M221C:CC, M221Dc:CC

59:C M221Aa:CCC, M221Ba:CCC

24:C 321A:CC

24:C 321A:CC

24:C 321A:CC

24:C 321A:CC

24:C 321A:CC

24:C 321A:CC

54:P, 55:C 232Bf:CCC

53:C 232Dc:CCC, 232Dd:CCC

55:C 232Bf:CCC

52:C 231Ad:CCC

40:C, 41:C 232Fa:CC, 232Fb:CCP, 232Fe:CCP

40:C, 41:C 231Ea:CCC, 231Ef:CCC, 232Fa:CCC, 232Fb:CCC, 232Fe:CCC

50:C 231D:CC

40:C, 41:C 231Ea:CCC, 231Eh:CCC, 232Fa:CCC, 232Fe:CCC

52:C 231A:CC

50:C, 59:C M221Ce:CCC

38:C, 39:C 222Ag:CPC, 222Am:CP?, 231G:CC, M222A:CC, M231A:CC
40:C, 41:C 231Ea:CCC, 231Eb:CCP, 231Ee:CC?, 231Eg:CC?, 231Ej:CCP, 231Ek:CCP, 231Em:CC?, 231En:CCP, 232Fa:CC

53:C 232Bg:CCC, 232Bj:CC?

54:P, 55:C 232Gc:CCC

54:C, 55:P 232Da:PPP, 411Af:CCC, 411Ag:CCC

54:C 411Af:CCC

53:C, 55:C, 56:C 232Ce:CCC, 232Dc:CCC, 232Gb:CCC

53:C 232B:CC, 232Dc:CCC

53:C 232Ba:CC?, 232Bh:CCC, 232Bj:CCC, 232Dc:CCC

53:P, 56:C 232Br:CCC, 232Ca:CCC

53:C 232Bj:CPP, 232Dc:CCC

53:C 232:C

56:C 232Br:CCC

55:C 232Db:CCC, 232Gb:CCC

56:C 232Br:CCC, 232Ca:CCC

57:C 232Ch:CCC

40:C, 41:C 231Ea:PPP, 232Fa:CCC, 232Fb:CCP, 232Fe:CCP

53:C 232Bb:CCC

50:C, 52:C 231Aa:CC?, 231Ab:CCC, 231Ac:CCC, 231Af:CCC, 231Ai:CCP, 231Aj:CCC, 231Ao:CC?, 231Bc:CCC, 231Bd:CC?

53:?, 56:C 232Ce:CCC

57:C 232Cb:CCC

57:C 232Cb:CCC, 232Ch:CCC

40:?, 41:C 232Fa:CCP, 232Fb:CCP, 232Fe:CCC

57:C 232:C

57:C 232:C

41:C 232Fa:CCP

57:C 232Cb:CCC

53:C 232Bg:CCC

55:C 232Bf:CCC

40:C, 41:C 232Fa:CCC, 232Fb:CCP, 232Fe:CCP

56:C 232Bn:CCP, 232Bq:CCC, 232Br:CC?

56:C 232Bq:CCC, 232Br:CCC, 232Ca:CCC

57:C 232Bq:CCC, 232Cb:CCP, 232Ch:CCP

40:C, 41:C 232Fa:CCC, 232Fb:CCP, 232Fe:CCP

57:C 232Bq:CCC

57:C 232Cb:CCC, 232Ch:CCC

56:C 232Bn:CCP, 232Bq:CCC, 232Br:CC?, 232Ca:CCC

43:?, 53:C, 56:C, 57:C 232Bq:CCC, 232Br:CCC, 232Cb:CCC, 232Ce:CCC

57:C 232Bq:CCC

56:C 232:C

53:C 232Bj:CCC, 232Dc:CCC

56:C 232Ca:CCC, 232Ce:CCC

53:C 232Bj:CCC

56:P, 57:C 232Cb:CCC, 232Ce:CCC

56:C 232Br:CCC

57:C 232Bq:CCC

41:C 232Fa:CCC

41:C 232Fa:CCC

53:C 232Bj:CCC

57:C 232Bq:CCC

56:P, 57:C 232Cb:CCC, 232Ce:CCC

53:C 232Bh:CCC

41:C 232Fb:CCC
53:C 232Ba:CCC

40:?, 41:C 231E:CC, 232F:CC

53:C 232Dc:CCC

41:C 231E:CC, 232F:CC

31:C, 41:C 232Ea:CCC, 232Eb:CCP, 232Fb:CCC

53:C, 55:C, 56:C 232Be:CCC, 232Bf:CCC, 232Bg:CCC, 232Bh:CCC, 232Bi:CCC, 232Bj:CCC, 232Bp:CCP, 232Ca:CCC, 232Cc:CC

53:C, 55:P, 56:C 232Ca:CCC, 232Cb:CCC, 232Cf:CCC, 232Dc:CCC

21:C, 24:C 321A:CC, M313B:CC

29:C 315D:CC

24:C 321A:CC

51:C M221Db:CCP, M221Dc:CCC, M221Dd:CCC

50:C M221Ce:CCC

56:C, 57:C 232Cb:CCC, 232Ce:CCC

53:P, 55:C, 56:P 232Bf:CCC

57:C 232Ch:CCC

57:C 232Ch:CCC

53:C 232Dc:CCC

50:C, 51:C 221Hc:CCC, M221Dc:CCC, M221Dd:CCC

40:C, 41:C 231Ea:CCC, 232Fa:CCC, 232Fe:CCC

57:C 232Ch:CCC

57:C, 58:C 232Br:CCC, 232Bx:CCC, 232Ch:CCC, 232Ci:CCC

53:C, 56:C, 57:C 232Dc:CCC

57:C 232Cb:CCC

50:P, 51:C 221Jb:PPP, M221Dd:CCC

51:C, 52:C M221Dc:CCC, M221Dd:CCC

30:C, 31:C 255Dc:CCC

30:C, 31:C 255Da:CCC, 255Dc:CCC, 315C:CC, 315D:CC, 315E:CC

44:C 222Eb:CCC, 222Eg:CC?, 222Eh:CC?

50:C 231De:CCC

52:C, 57:C, 58:C 231Ae:CCC, 231Ak:CCC, 231An:CCC, 232Br:CCC, 232Bz:CCC, 232Ch:CCC, 232Cj:CCC

52:C 231Aa:CCP, 231Af:CCC

51:C M221Dc:CCC, M221Dd:CCC

40:C 231Eh:CCC

52:C 231Af:CCC

52:C 231Aa:CCC, 231Ae:CCP, 231Af:CCC

40:C 231Ed:CCC, 232Fa:CCC

51:C M221Dc:CCC, M221Dd:CCC

40:C 231Ea:CCP, 231Eg:CC?, 231Ej:CCC, 231Ek:CCC

32:C 255Af:CCC

56:?, 57:C 232Cb:CCC

43:C, 44:C 222Cb:CCC, 222Cc:CCP, 222Ce:CCP, 222Cg:CCC, 222Da:CCC, 222Dg:CCC, 222Eg:CCC, 231Ba:CCC, 231Bk:C

29:?, 33:C 311A:CC

31:C 255Dc:CCC

54:?, 55:C, 56:C 232Ce:CCC, 232Gb:CCC

55:C 232Bf:CCC

53:C, 55:C 232Dc:CCC

53:C 232Bg:CCC, 232Bj:CCC, 232Dc:CCC

55:C 232Bf:CCC, 232Ga:CCC

53:C 232Bg:CCC

56:C, 57:C 232Cb:CCC, 232Ce:CCC

53:C, 56:C 232Bh:CCC, 232Br:CCC, 232Bs:CC?, 232Ca:CCC, 232Cb:CCC

29:C 315D:CC
43:C, 53:C 232Ba:CCC, 232Bb:CCC, 232Bc:CCC, 232Bd:CCC, 232Be:CCC, 232Bj:CCC, 232Dc:CCC

56:C, 57:C 232Cb:CCC, 232Ch:CCC

43:C, 44:C 222C:CC, 222D:C?, 222Eg:CCP, 222Eh:CCC

42:C 234Ac:CCC

40:C 231E:CC

38:C, 39:P, 42:C M222Aa:CCC

44:C 222Eg:CCC

53:C 232Dc:CCC

57:C, 58:? 232Ch:CCC

56:P, 57:C 232Bs:CCC

44:C 222Dg:CCC

56:C 232Br:CCC

29:C 315D:CC

53:C, 55:P, 56:P 232Bg:CCP, 232Dc:CCC

56:P, 57:C 232Cb:CCC

53:C 232Ba:CCP, 232Bj:CCP, 232Dc:C??

56:C 232Cb:CCC, 232Ce:CCC

52:C, 58:C 231Af:CCP, 231Ao:CCC

52:C, 59:C 231Ae:CCC, 231Ap:CCC, M221Ab:CCC

38:C 222Ag:CCC, 222An:CCC, M222Ab:CCC

44:C 222Eb:CCC

40:C, 41:C, 43:? 232F:CC

52:C, 57:C, 61:C 221Db:CCC, 231Ae:CCC, 231Af:CCC, 231Ak:CCC, 231Ap:CCC, 232Bs:CCC

52:C 231Ad:CCC, 231Af:CCC

44:C, 50:C 221E:CC

50:P, 51:C, 59:? M221Dc:CCC, M221Dd:CCC

51:C M221Dc:CCC

44:C, 50:C 221Hc:CCC, 222Dg:CCC, 222Eb:CC?, 222Ec:CCC, 222Ed:CC?, 222Ee:CC?, 222Ef:CCC, 222Eg:CCP, 222Eh:CC

44:C 222Eb:CCC, 222Eg:CC?

52:C 231Af:CCC

52:C 231Aa:CCC

52:C 231A:CC

32:?, 40:C, 41:C 231Ea:CCC, 231Ed:CCC, 231Eh:CCP, 232Fe:CCC

39:C 231Gb:CCC, M231Aa:CCC

43:C 231Ba:CCC

39:C M231A:CC

44:C 222Ed:CCC

44:C 222Dg:CCC, 222Dj:CCC, 222Ec:CCP, 222Eg:CCC, 222Eh:CCC

31:C 231Fb:CCC, 255Dc:???

31:C, 53:C 231Fb:PPP, 232Dc:CCC, 232Eb:CCC, 232Ec:CCC, 255Dc:PPP

53:C, 55:C, 56:C, 57:C 232Ce:CCC, 232Ci:CCC, 232Dc:CCC, 232Gb:CCC

31:C 231Fb:CCC, 255Da:CCC, 255Db:CCC, 255Dc:CCP

31:C 231Fb:PPP, 232Eb:CCC

53:C 232Dc:CCC

56:C, 57:C 232Cb:CCC, 232Ch:CCC, 232Ci:CCC

56:C, 57:C 232Ci:CCC

31:C 232Ea:CCC, 232Eb:CCC

31:C 231Fa:CCC, 231Fb:CCC, 255Da:CCC, 255Db:CCC, 255Dc:CCC, 255Dd:CCC

31:C 232Ea:CCC, 232Eb:CCC

31:C 255Da:CCC, 255Db:CCC

53:C, 55:C, 56:C 232Ce:CCC, 232Dc:CCC, 232Gb:CCC

54:C 411Ae:CCP, 411Ag:CCC
54:C 411A:CC

30:C, 31:C 315E:CC

53:P, 55:P, 56:C, 57:P 232Ce:CCC, 232Da:CPP, 232Dc:CPP, 232Ga:CP?, 232Gb:CPP

53:C, 55:C, 56:C 232Cb:CC?, 232Ce:CCC, 232Db:CPP, 232Dc:CPP, 232Ga:CCC, 232Gb:CCC, 232Gc:CCP, 232Gd:CCP

55:C 232Db:CPP, 232Ga:CCC, 232Gb:CCC, 232Gc:CCP, 232Gd:CCP

54:C 411A:CC

53:P, 55:C, 56:C 232Bf:CCC, 232Ce:CCC, 232Gb:CCC

56:?, 57:C 232Ce:CCP, 232Ci:CCC

24:C 321A:CC

24:C 321A:CC

53:C 232Dc:CCC

54:C 411A:CC

54:C 411A:CC

56:P, 57:C 232Cb:CCC, 232Ce:CCC

54:C 411A:CC

57:C 232Bv:CCC

56:C, 57:C 232Bq:CCP, 232Bv:CCC, 232Cb:CCC, 232Ce:CCC

54:C 411A:CC

54:C 411A:CC

56:P, 57:C 232Bv:CCC, 232Cb:CCC

53:C 232Db:CC?, 232Dc:CCC, 232Dd:CC?

55:C, 56:C 232Bf:CCC, 232Ca:CCC, 232Cd:CCC, 232Ce:CCC

53:C 232Dc:CCC

57:C, 58:? 232Ch:CCC

29:C 315D:CC

39:C 231Ga:???, M231Ac:CCC, M231Ad:CCC

57:C, 58:C 232Br:CCC, 232Bt:CCC, 232Bx:CCC, 232Ch:CCC

54:C 411Af:CCC

57:C, 58:? 232Cb:CCC, 232Ch:CCC, 232Ci:CCP

43:C, 53:C 231Bd:CCC, 232Bl:CCC

51:C, 52:C 231Ab:CCC, 231Ad:CCC, M221Dc:CCC, M221Dd:CCC

50:C, 51:C, 52:C, 59:C M221Aa:CCC, M221Ac:CCC, M221Bb:CCP, M221Bf:CCC, M221Cc:CCC, M221Da:CCP, M221Db:CCC, M221Dc:C

50:C, 59:C M221Aa:CCC, M221Da:CCC

51:C M221Dd:CCC

51:C, 52:C 231Aa:CCC, M221Db:CCP, M221Dc:CCC, M221Dd:CCC

51:C, 52:C, 59:C 231Aa:CCC, 231Ae:CCP, M221Aa:CC?, M221Ab:CCC, M221Da:CCC, M221Db:CCP, M221Dc:CCC, M221Dd:CCC

29:?, 30:?, 31:C, 32:P 232F:??, 255Ah:CPP, 255Ai:CPP, 255Ba:CPP, 255Ca:CPP, 255Db:CCC

3:C, 5:?, 81:C M242B:CC, M261A:??, M261D:??

1:C, 5:C M242A:CC, M261A:CC

1:C, 5:C M242A:CC, M261A:CC

4:C, 5:C M261G:CC

5:C M261A:CC

5:C M261A:CC

20:C, 27:P 311:C, 331I:CC, M331F:CC, M331G:CC

4:C M242C:CC, M261G:CC

4:C M242C:CC, M261G:CC

20:C M331G:CC, M331I:CC

21:C M313A:CC

20:?, 21:C, 22:C M313A:CC, M331G:??

4:C M242C:CC, M261G:CC

3:C, 4:C, 81:C M242B:CC, M242C:CC

4:C M242C:CC
1:C, 2:C, 3:C, 81:C 242A:CC, M242A:CC, M242B:CC

4:C M242C:CC

8:C M332A:CC, M332G:CC

2:?, 4:C 242A:??, M242C:CC

4:?, 7:C, 8:C, 68:? M242C:??, M332A:CC, M332B:CC, M332G:CC, M333A:C?, M333D:CC

7:C, 8:C, 68:C M332A:CC, M332B:CC, M332G:CC, M333A:CC, M333B:C?, M333C:CC, M333D:CC

6:?, 8:C M332A:CC, M332G:CC

4:C M242C:CC

1:C M242A:CC

21:C M313A:CC

2:C 242A:CC

10:C, 18:C, 19:C, 20:C 341B:CC, 342G:CC, M331G:CC, M331H:CC, M341B:CC

6:C, 9:C, 10:C, 19:C, 26:C 331G:CC, 342A:CC, 342B:CC, M331D:CC, M331E:CC

6:C, 9:C 331A:CC, M331D:CC

6:? M332G:CC

6:C, 8:C, 19:C 331A:CC, 342C:CC, 342H:CC, 342I:CC, M332G:CC

6:C 342B:CC, 342C:CC, M332G:CC

6:C, 8:C, 11:C 342B:CC, 342C:CC, M332G:CC

1:?, 5:C M242A:??, M261A:CC

1:C, 5:C, 14:C, 15:C 263A:CC, M261A:CC

24:C 321A:CC

21:P, 22:?, 24:C 321A:CC

5:C, 13:C, 14:C 263A:CC, M261A:CC, M261C:CC, M261D:CC, M261F:CC

13:C, 14:C 262A:CC, 263A:CC, M261C:CC

2:C 242A:CC

2:C 242A:CC

21:C, 22:?, 24:P 313:?, 321A:PP, M313A:CC

6:C 342H:CC, M332G:CC

6:C 341:C, 342B:CC, 342C:CC, M332G:??

6:?, 9:C, 10:C, 19:C 341B:CC, 342F:CC, 342G:CC, M331E:CC

22:C, 24:? 313C:CC, 321A:??, M313B:CC

9:?, 10:C 342A:CC, M331B:??

20:C, 27:C 331H:CC, M331:C

10:?, 20:C M331I:CC

27:C 331H:CC

7:C M332C:CC, M333B:CP, M333C:CC, M333D:CP

4:C M242C:CC

65:C M423:C

8:C, 9:C M331A:CC, M331D:CC, M332B:CC, M332C:CC, M332E:CC

7:C M333B:CC, M333C:CC

21:P, 22:P, 24:P 321A:CC, M313B:CC

4:C, 8:C, 9:C M331A:CC, M331D:CC, M331J:CC, M332E:CC

19:P, 21:P M313A:CC

10:C, 20:C M331I:CC

20:C M331I:CC

10:C, 19:C M331E:CC

M331:C

1:C, 2:C, 14:C 242A:CC, 263A:CC, M242A:CC

1:C, 2:C 242A:CC, M242A:CC

69:C M245A:CC

6:C, 7:C, 8:C, 9:C M331A:CC, M332C:CC, M332D:CC, M332E:CC, M332G:CC

4:C, 11:C M242C:CC
4:C, 68:C M242C:CC, M333A:CC

10:C, 20:C M331H:CC, M331I:CC

5:C M261A:CC, M261D:C?

2:C 242A:CC

1:C M242A:CC

24:C 321A:CC

24:C 321A:CC

24:C 321A:CC

19:C, 20:C 313A:CC, 341B:CC, M331G:CC

27:?, 28:C 315A:CC, 331I:??, M313B:??

19:C 313B:CC

24:C 321A:CC

5:C M261A:CC

14:P, 15:C 263A:CC

4:C, 8:C M242C:CC, M332G:CC

4:C, 5:C M242C:CC, M261A:CC, M261D:C?

4:C M242C:CC

4:C M242C:CC

4:C M242C:CC

2:C, 4:C, 5:C, 81:C M242C:CC, M261A:CC, M261D:CC, M261G:C?

26:C 331G:CC

20:C M331I:CC

8:?, 26:C 331D:CC, M332D:??

4:?, 5:C M261A:CC, M261D:CC, M261G:C?

8:C, 9:C 342:C, M331J:CC

4:C, 6:C, 8:C 342C:CC, M242C:CC, M261G:CC, M332G:CC

4:C, 6:?, 8:C M242C:CC, M332G:CC

8:C M332G:CC

22:C 313C:CC

6:C, 7:C, 8:C, 68:C 331A:CC, 342I:CC, M332A:CC, M333A:CC, M333D:CC

4:C M242C:CC

4:C M242C:CC

6:P, 8:C M332G:CC

4:C M242C:CC

21:P, 24:P 321A:CC, M313A:CC

21:C, 22:?, 24:C 321A:CC, M313A:CC

313:C, 321:C, M313:C

9:C, 10:C, 18:C, 19:C, 20:C M331E:CC, M331H:CC, M331I:CC, M341B:CC

6:C, 9:C 342B:CC, M331D:CC

9:P, 10:C, 20:C, 26:C 342A:CC, M331B:CC, M331I:CC

10:C, 17:C, 19:C, 20:C 313A:CC, 322A:CC, 341B:CC, M331G:CC

20:C, 27:C 331I:CC

3:P, 4:C, 6:C, 7:C, 8:C, 9:C, 10:C, 81:C 342A:CC, 342B:C?, 342C:CC, 342H:C?, 342I:CC, M242B:C?, M242C:CC, M331D:CC, M332G:CC, M333C:CC

7:C, 8:C M332B:CC, M332C:CC, M332D:C?, M333B:CC, M333C:CC

2:C 242A:CC

1:?, 2:C, 3:?, 81:? 242A:CC, M242A:??, M242B:??

1:C M242:C

68:C M333A:CC

21:C, 24:C, 28:C 313:C, 315:?, 321:C, M313:?

19:C 313A:CC, 341B:CC, M313:?

9:C, 27:C 331I:CC, M331E:CC

19:C, 20:C 313:C, M313:?
20:C, 21:C 313:C, 315:?, 321:C, M313:?

27:C 331C:CC, 331H:CC

8:C, 9:C, 10:C, 26:C 331D:CC, 331G:CC, 342A:??, M331A:CC, M331B:C?, M332D:CC

28:C 313:?, 315:C, 331:?, M313:?

21:C, 24:C 313:C, 315:?, 321A:CC, M313:?

24:C 321:C

9:C, 10:C, 18:C, 19:C, 20:C 313A:CC, 341B:CC, M331E:CC, M341B:CC

20:C 313:C, M313:C

24:C 321:C

19:C, 21:C, 22:C, 24:? 313A:CC, 321A:CC, M313A:CC, M313B:C?

21:P, 24:P 321A:CC, M313A:CC

21:C, 22:P, 24:P 321A:CC, M313A:CC

21:P, 24:P 321A:CC, M313A:CC

19:C, 21:C, 22:C, 23:?, 24:C 321A:CC, 322B:C?, 341B:CC, M313A:CC

11:C, 17:C, 19:C, 24:C 321A:CC, 322A:CC, 341B:CC

15:C, 16:C, 17:C, 19:C, 21:P, 22:P, 24:C 321A:CC, 322:C, M262A:CC, M262B:CC

21:C, 24:C 321A:CC, M313A:CC

9:C M331D:CC

6:P, 9:C, 11:C, 18:C, 19:C, 20:C 342B:CC, M331F:CC, M341A:CC

9:C, 10:C, 19:C M331D:CC, M331E:CC

2:C 242A:CC

4:C, 6:C, 8:C, 68:C 342B:CC, 342H:CP, 342I:CP, M242C:CC, M332G:CC, M333A:CC

9:C, 20:C M331D:CC, M331E:CC, M331H:CC

9:C M331D:CC

18:C, 20:C M331F:CC, M341C:CC

9:C M331D:CC, M331J:CC

9:C, 20:C M331D:CC, M331F:CC

65:C M423:C

1:C, 2:C, 4:?, 5:C, 14:C, 81:C 242A:CC, M242C:??, M261A:CC, M261B:CC

14:C 263A:CC

1:C, 14:C 263A:CC

2:C, 3:C, 5:C, 81:C 242A:CC, M242B:CC, M261A:CC

2:C 242A:CC

1:C M242A:CC

2:C 242A:CC

9:C, 20:C, 26:C 331D:CC, M331D:CC, M331E:CC, M331G:CC

4:C M242C:CC

1:?, 2:C 242A:CC, M242A:??

9:C, 10:C 342A:CC, M331B:CC

9:C, 10:C, 19:C, 20:C M331D:CC, M331H:CC, M331I:CC

26:C 331D:CC, M332:?

22:P, 24:P 313C:CC, 321A:CC

1:C, 2:C 242A:CC, M242A:CC

2:C, 4:C, 8:C, 81:C M242C:CC

21:C, 22:C, 24:C 321A:CC, M313A:CC

2:C 242A:CC

1:?, 2:C, 5:C, 14:? 242A:CC, M242A:??, M261A:CC, M261B:C?, M261D:C?

2:C, 5:C, 14:? 242A:CC, M261A:CC, M261B:C?, M261D:CC

2:C 242A:CC

2:C 242A:CC

4:C M242C:CC

1:C, 2:C, 4:C, 5:C, 81:C 242A:CC, M261A:CC, M261D:C?
12:C, 14:C, 15:C, 16:C 261A:CC, 261B:CC, 263A:CC, M261C:CC, M261E:CC, M262A:CC, M262B:CC

16:C 261B:CC

2:C 242A:CC

65:C M423A:CC

1:C, 3:C, 5:C, 81:C M242B:CC, M261A:CC, M261D:CC

3:C, 81:C M242B:CC

7:C, 8:C M332A:CC, M333D:CC

7:C, 68:C M333A:CC, M333B:CC, M333C:CC, M333D:CP

3:C, 4:C, 81:C M242B:CC, M242C:CC

7:C, 8:C, 68:C M332A:CC, M333A:CC, M333B:CC, M333D:CC

7:C, 68:C M333A:CC, M333B:CC

5:C M261A:CC

68:C M333A:CC

68:C M333A:CC

7:C, 68:C M333A:CC, M333B:CC, M333D:CC
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Bourgeron and Engelking 1994, Driscoll et al. 1984, Hawk 1977, Kagan et al. 1998, Kagan et al. 2000, Western Ecology Working Group n.d., Wiedemann 19

Bourgeron and Engelking 1994, Driscoll et al. 1984, Hawk 1977, Kagan et al. 2000, Western Ecology Working Group n.d., Whittaker 1960

Atzet et al. 1996, Bourgeron and Engelking 1994, Driscoll et al. 1984, Franklin and Dyrness 1973, Hawk 1977, Kagan et al. 2000, Western Ecology Working 

Atzet et al. 1996, Bourgeron and Engelking 1994, Driscoll et al. 1984, Hawk 1977, Kagan et al. 2000, Western Ecology Working Group n.d.

Atzet and McCrimmon 1990, Hawk 1977, Jimerson 1994, Jimerson et al. 1995, Kagan et al. 2004, Western Ecology Working Group n.d.

Bourgeron and Engelking 1994, Christy et al. 1998, Driscoll et al. 1984, Hawk 1977, Jimerson 1994, Kagan et al. 2000, ORNHP unpubl. data, Randall 1996, 

Western Ecology Working Group n.d.

Western Ecology Working Group n.d.

Western Ecology Working Group n.d.

Christy 2004, Christy and Putera 1993, Kagan et al. 2000, Kunze 1994, Titus et al. 1996, WNHP unpubl. data, Western Ecology Working Group n.d.

Western Ecology Working Group n.d.

Western Ecology Working Group n.d.

Bourgeron and Engelking 1994, Driscoll et al. 1984, Kagan et al. 2000, Western Ecology Working Group n.d., Wiedemann 1966, Wiedemann 1984

Boggs 1996, Bourgeron and Engelking 1994, Pawuk and Kissinger 1989, Western Ecology Working Group n.d.

Christy et al. 1998, Duebendorfer 1992, Egler 1934, Kagan et al. 2000, Kumler 1969, Western Ecology Working Group n.d., Wiedemann 1984, Wiedemann 1

Alpert 1984, Bourgeron and Engelking 1994, Christy et al. 1998, Driscoll et al. 1984, Duebendorfer 1992, Egler 1934, Kagan et al. 2000, Kumler 1969, Weste

Bourgeron and Engelking 1994, Driscoll et al. 1984, Jenny et al. 1969, Kagan et al. 2000, Martin and Frenkel 1978, Western Ecology Working Group n.d.

Bourgeron and Engelking 1994, Chappell 1994, Douglas 1971, Driscoll et al. 1984, Franklin and Dyrness 1973, Krajina 1969, Western Ecology Working Grou

Bassett et al. 1987, Bourgeron and Engelking 1994, Bourgeron et al. 1993b, Bourgeron et al. 1995, Driscoll et al. 1984, Muldavin et al. 1996, NMNHP unpubl

Bourgeron and Engelking 1994, Bourgeron et al. 1993b, Driscoll et al. 1984, NMNHP unpubl. data, Western Ecology Working Group n.d.

Bourgeron and Engelking 1994, Bourgeron et al. 1993b, Driscoll et al. 1984, NMNHP unpubl. data, Western Ecology Working Group n.d.

Bourgeron and Engelking 1994, Day 1985, Day and Wright 1985, Driscoll et al. 1984, Eggler 1941, Western Ecology Working Group n.d.

Atzet and Wheeler 1984, Atzet et al. 1996, Bourgeron and Engelking 1994, Driscoll et al. 1984, Kagan et al. 2000, ORNHP unpubl. data, Western Ecology W

Kunze 1994, Western Ecology Working Group n.d.

Bourgeron and Engelking 1994, Driscoll et al. 1984, Kagan et al. 2000, ORNHP unpubl. data, Western Ecology Working Group n.d.
Bourgeron and Engelking 1994, Dealy 1971, Driscoll et al. 1984, Dyrness 1960, Dyrness and Youngberg 1966, Franklin et al. 1972, Johnson 1961a, Kagan e

Berry 1963, Bourgeron and Engelking 1994, Driscoll et al. 1984, Kagan et al. 2000, Moir et al. 1973a, Western Ecology Working Group n.d.

Bourgeron and Engelking 1994, Driscoll et al. 1984, Lillybridge et al. 1995, Western Ecology Working Group n.d., Williams and Smith 1990

WNHP unpubl. data, Western Ecology Working Group n.d.

Bourgeron and Engelking 1994, Daubenmire 1952, Daubenmire and Daubenmire 1968, Driscoll et al. 1984, Franklin and Dyrness 1973, Steele et al. 1981, W

Berry 1963, Bourgeron and Engelking 1994, Clausnitzer and Zamora 1987, Driscoll et al. 1984, Kagan et al. 2000, Moir et al. 1973a, Moir et al. 1973b, Weste

Bourgeron and Engelking 1994, Driscoll et al. 1984, Hoffman and Alexander 1976, Hoffman and Alexander 1987, Johnston 1987, Jones and Fertig 1998a, Jo

Cheatham and Haller 1975, Griffin and Critchfield 1972, Grossman et al. 1994, Jones and Stokes Association, Inc. 1996, Sawyer and Keeler-Wolf 1995, Vog

Cheatham and Haller 1975, Griffin and Critchfield 1972, Grossman et al. 1994, Keeler-Wolf 1990, Rundel et al. 1988, Sawyer and Keeler-Wolf 1995, Wester

Western Ecology Working Group n.d.

Baker 1986, Baker 1989b, Bourgeron and Engelking 1994, CONHP unpubl. data 2003, Carsey et al. 2003a, Driscoll et al. 1984, Kittel et al. 1994, Kittel et al. 

BCMFRB 2003a, BCMFRB 2005b, BCMWLAP 2004a, BCMWLAP 2004e, Brown and Hebda 1999, COSEWIC 2002, Cadrin and Wolowicz 2005, Green and 

Bourgeron and Engelking 1994, Daubenmire 1970, Driscoll et al. 1984, Evans 1989a, IDCDC 2005, WNHP unpubl. data, Western Ecology Working Group n

Christy 2001a, Christy 2004, Christy and Putera 1993, Kagan et al. 2000, Kunze 1994, WNHP unpubl. data, Western Ecology Working Group n.d.

Bourgeron and Engelking 1994, Crowe et al. 2004, Driscoll et al. 1984, IDCDC 2005, Jankovsky-Jones et al. 2001, Kagan et al. 2000, Kauffman 1982, Kauffm

Bourgeron and Engelking 1994, Driscoll et al. 1984, IDCDC 2005, Kagan et al. 2000, Manning and Padgett 1992, Manning and Padgett 1995, Poulton 1955, 

Bourgeron and Engelking 1994, CONHP unpubl. data 2003, Carsey et al. 2003a, Carsey et al. 2003b, Driscoll et al. 1984, Kittel et al. 1999b, Powell 1988a, R

Bourgeron and Engelking 1994, Driscoll et al. 1984, Kagan 1985, Kagan et al. 2000, Western Ecology Working Group n.d.

Western Ecology Working Group n.d.

Western Ecology Working Group n.d.

Western Ecology Working Group n.d.

Western Ecology Working Group n.d.

Western Ecology Working Group n.d.

Western Ecology Working Group n.d.

Western Ecology Working Group n.d.

Chappell et al. n.d., WNHP unpubl. data, Western Ecology Working Group n.d.

Bourgeron and Engelking 1994, Driscoll et al. 1984, Fonda and Bernardi 1976, Franklin and Dyrness 1973, Krajina 1969, Rapp 1981, Western Ecology Work

Bourgeron and Engelking 1994, Driscoll et al. 1984, Lillybridge et al. 1995, Western Ecology Working Group n.d., Williams and Smith 1990

Bourgeron and Engelking 1994, Driscoll et al. 1984, Fonda and Bernardi 1976, Franklin and Dyrness 1973, WNHP unpubl. data, Western Ecology Working G

Bourgeron and Engelking 1994, Bourgeron et al. 1993b, Bourgeron et al. 1995, Driscoll et al. 1984, Reid et al. 1994, UNESCO 1973, Western Ecology Work

Bourgeron and Engelking 1994, Driscoll et al. 1984, Franklin and Dyrness 1973, John and Tart 1986, John et al. 1988, Lillybridge et al. 1995, WNHP unpubl. 

Bourgeron and Engelking 1994, Driscoll et al. 1984, John and Tart 1986, Kagan et al. 2000, WNHP unpubl. data, Western Ecology Working Group n.d.

Bourgeron and Engelking 1994, Driscoll et al. 1984, ORNHP unpubl. data, Thilenius 1968, WNHP unpubl. data, Western Ecology Working Group n.d.

Bourgeron and Engelking 1994, Driscoll et al. 1984, John and Tart 1986, Kagan et al. 2000, Lillybridge et al. 1995, ORNHP unpubl. data, WNHP unpubl. data

Chappell et al. n.d., WNHP unpubl. data, Western Ecology Working Group n.d.

Bourgeron and Engelking 1994, Driscoll et al. 1984, Webb and Brotherson 1988, Western Ecology Working Group n.d.

Western Ecology Working Group n.d.

Western Ecology Working Group n.d.

Bourgeron and Engelking 1994, Chappell 1994, Chappell 1997, Chappell 2006b, Driscoll et al. 1984, Fonda and Bernardi 1976, Franklin and Dyrness 1973, G

Bourgeron and Engelking 1994, Chappell 1997, Chappell 2006b, Driscoll et al. 1984, Fonda and Bernardi 1976, Franklin and Dyrness 1973, Henderson et al

Kunze 1994, WNHP unpubl. data, Western Ecology Working Group n.d.

Bourgeron and Engelking 1994, Christy 2001a, Christy 2004, Driscoll et al. 1984, Franklin 1966, Glad et al. 1987, Howarth 1995, Kagan et al. 2000, Western 

Bourgeron and Engelking 1994, Driscoll et al. 1984, Western Ecology Working Group n.d., Williams and Lillybridge 1985

BCMFRB 2003a, BCMFRB 2005a, BCMFRB 2005b, BCMWLAP 2004a, BCMWLAP 2004d, BCMWLAP 2004e, Banner et al. 1983, Banner et al. 1989, Bann

BCMFRB 2003a, BCMFRB 2005a, BCMFRB 2005b, BCMWLAP 2004b, BCMWLAP 2004d, Banner et al. 1993, Cadrin and Wolowicz 2005, Dorner and Won

BCMFRB 2003a, BCMFRB 2005a, BCMFRB 2005b, BCMWLAP 2004a, BCMWLAP 2004b, BCMWLAP 2004c, BCMWLAP 2004d, Banner et al. 1993, Bann

BCMFRB 2003a, BCMFRB 2005a, BCMFRB 2005b, BCMWLAP 2004d, Brown and Hebda 1999, Cadrin and Wolowicz 2005, Chappell 1997, Chappell 2005

BCMFRB 2003a, BCMFRB 2005a, BCMFRB 2005b, BCMWLAP 2004d, Brown and Hebda 1999, Green and Klinka 1994, Meidinger et al. 2005, Western Eco

BCMFRB 2003a, BCMFRB unpubl. data 1992, BCMWLAPPPA 2003, DeLong et al. 1993, Parminter 1995, Steen and Coupe 1997

BCMF and BCMELP 1995, BCMFRB 2003a, BCMFRB 2003b, BCMFRB 2005a, BCMFRB 2005b, Cadrin and Wolowicz 2005, Green and Klinka 1994, Meidi

BCMFRB 2003a, BCMFRB 2005a, BCMFRB 2005b, BCMWLAP 2004b, BCMWLAP 2004d, Brown and Hebda 1999, Cadrin and Wolowicz 2005, Green and 

BCMFRB 2003a, BCMFRB 2005a, BCMFRB 2005b, Banner et al. 1993, Cadrin and Wolowicz 2005, Dorner and Wong 2003, Green and Klinka 1994, Lewis 
BCMFRB 2003a, BCMFRB 2005a, BCMFRB 2005b, BCMWLAP 2004b, BCMWLAP 2004d, BCMWLAP 2004e, Banner et al. 1993, Bigley and Hull 1995, Bro

BCMFRB 2003a, BCMFRB 2005a, BCMFRB 2005b, Eng unpubl. data 2005, Green and Klinka 1994, Meidinger et al. 2005, Western Ecology Working Group 

BCMFRB 2003a, BCMFRB 2005a, BCMFRB 2005b, Cadrin and Wolowicz 2005, Green and Klinka 1994, Klinka et al. 1997, Kojima and Krajina 1975, Meidin

BCMFRB 2003a, BCMFRB 2005a, BCMFRB 2005b, BCMWLAP 2004b, BCMWLAP 2004f, Banner et al. 1983, Banner et al. 1989, Cadrin and Wolowicz 200

BCMFRB 2003a, BCMFRB 2005a, BCMFRB 2005b, Banner et al. 1993, Cadrin and Wolowicz 2005, Dorner and Wong 2003, Green and Klinka 1994, Lewis 

BCMFRB 2003a, BCMFRB 2005a, BCMFRB 2005b, Cadrin and Wolowicz 2005, Green and Klinka 1994, Klinka et al. 1997, Kojima and Krajina 1975, Meidin

BCMFRB 2003a, BCMFRB 2005a, BCMFRB 2005b, Green and Klinka 1994, Meidinger et al. 2005, Western Ecology Working Group n.d.

BCMFRB 2003a, BCMFRB 2005a, BCMFRB 2005b, Banner et al. 1993, Dorner and Wong 2003, Eng unpubl. data 2005, Green and Klinka 1994, Lertzman e

Byers et al. 2007, Ceperley 2002, Eastern Ecology Working Group n.d., Fortney et al. 2005

Byers et al. 2007, Ceperley 2002, Eastern Ecology Working Group n.d., Fortney 1975, Fortney et al. 2005

Eastern Ecology Working Group n.d., Fleming 2001a, Fleming et al. 2001, Harrison 2004, VDNH 2003

Breden 1988, Breden 1989, Breden et al. 2001, Eastern Ecology Working Group n.d., Edinger et al. 2002, Metzler and Barrett 2001, Rawinski 1984, Reschke 

Breden et al. 2001, Strakosch-Walz 2004

Breden 1989, Breden et al. 2001, Eastern Ecology Working Group n.d., Edinger et al. 2002, Enser 1993, Karlin 1988, Metzler 1997, Metzler and Barrett 2001

Breden 1989, Breden et al. 2001, Eastern Ecology Working Group n.d., Eyre 1980, Fike 1999, Grossman et al. 1994, Lee 1985, Livingston and Lund 1982, M

Eastern Ecology Working Group n.d., Edinger et al. 2002, Eyre 1980, Metzler and Barrett 2004, Rawinski 1984, Swain and Kearsley 2001, Thompson 1996, 

Bowman 2000, Breden 1989, Breden et al. 2001, Clancy 1996, Eastern Ecology Working Group n.d., Edinger et al. 2002, Fleming et al. 2001, Greller 1977, H

Allard 1990, Anderson 1990, Anderson et al. 1990, Byers et al. 2007, CAP pers. comm. 1998, Eastern Ecology Working Group n.d., Eyre 1980, Fike 1999, F

Byers et al. 2007, Darlington 1943, Eastern Ecology Working Group n.d.

Byers et al. 2007, Davis pers. comm., Eastern Ecology Working Group n.d., Fike 1999, Walbridge 1982, Walbridge and Lang 1982, Wieder et al. 1981

Eastern Ecology Working Group n.d.

Breden 1989, Breden et al. 2001, Eastern Ecology Working Group n.d., Windisch 1995b

Eastern Ecology Working Group n.d., NatureServe 2005, Windisch 1995b

Eastern Ecology Working Group n.d., Gawler 2000, Gawler 2002, Hill 1923, Moore and Taylor 1927, NAP pers. comm. 1998

Art 1976, Bennett et al. 1998, Bowman 2000, Breden 1989, Breden et al. 2001, Clancy 1996, DNHP 1998, Dowhan and Rozsa 1989, Eastern Ecology Worki

Breden 1989, Breden et al. 2001, Eastern Ecology Working Group n.d., Windisch 1995b

Breden et al. 2001, Eastern Ecology Working Group n.d., Edinger et al. 2002

Eastern Ecology Working Group n.d., Fike 1999, Grossman et al. 1994, Metzler and Barrett 2001, Motzkin 1993, Olsvig 1980, Pesiri 1982, Rawinski 1984, Re

Eastern Ecology Working Group n.d., Gawler 1991, Gawler 2002, Grossman et al. 1994, Harris 1991, Schweitzer and Rawinski 1988, Sperduto 1992, Widoff 

Eastern Ecology Working Group n.d., Grossman et al. 1994, Nichols et al. 2001, Rawinski 1984, Rawinski 1985, Sperduto 1992, Sperduto 2000a, Swain and 

Bartgis 1986, Bratton and Davison 1987, Breden et al. 2001, Clampitt 1991, Clancy 1993a, Clancy 1993b, Clancy 1996, Eastern Ecology Working Group n.d

Eastern Ecology Working Group n.d., Fleming et al. 2004, Lea 2000, Lea 2003

Breden et al. 2001, Eastern Ecology Working Group n.d., Walz et al. 2001

Art 1987, Bellis 1992, Breden 1989, Breden et al. 2001, Burk 1968, Dowhan and Rozsa 1989, Dunlop and Crow 1985, Eastern Ecology Working Group n.d., 

Bartgis 1993, CAP pers. comm. 1998, Eastern Ecology Working Group n.d., Fleming 1999, Fleming et al. 2001, Fleming pers. comm., Grossman et al. 1994

Coulling 1999, Eastern Ecology Working Group n.d., Fleming et al. 2004, Lea 2003, Nemeth 1973, Prentice et al. 1991

Girard et al. 1989, Johnston 1987, Jones 1992b, McAdams et al. unpubl. data 1998, Midwestern Ecology Working Group n.d., NDNHI n.d.

Girard 1985, Girard et al. 1989, Greenall 1995, Greenall 1996, Midwestern Ecology Working Group n.d., NDNHI n.d., Wali et al. 1980

Anderson 1996, Chapman et al. 1989, Homoya et al. 1988, Lindsey et al. 1969, Midwestern Ecology Working Group n.d.

Braun 1950, Cain 1935, Chapman et al. 1989, Crumpacker et al. 1988, Dodge and Harman 1985, Edinger et al. 2002, Kuchler 1964, Midwestern Ecology Wo

Anderson 1996, Harrison 2004, Midwestern Ecology Working Group n.d., TDNH unpubl. data

Butler 1983, Daubenmire 1970, Daubenmire and Daubenmire 1968, Driscoll et al. 1984, Girard et al. 1989, Godfread 1976, Godfread 1994, Hansen and Hoff

Anderson 1982, Chapman et al. 1989, MNNHP 1993, Midwestern Ecology Working Group n.d., Sytsma and Pippen 1981a, Sytsma and Pippen 1981b, WNH

Driscoll et al. 1984, Hoffman and Alexander 1987, Johnston 1987, Midwestern Ecology Working Group n.d., Thilenius 1970

BHCI unpubl. data 1999, Girard unpubl. data 1991, Hoffman and Alexander 1987, Marriott and Faber-Langendoen 2000, Marriott et al. 1999, Midwestern Eco

Chapman et al. 1989, Edinger et al. 2002, Midwestern Ecology Working Group n.d., Reschke et al. 1999

Blair and Hubbell 1938, Hoagland 2000, Hoagland pers. comm., Leahy pers. comm., Midwestern Ecology Working Group n.d., Rice 1963, Zollner pers. comm

Cahayla-Wynne and Glenn-Lewis 1978, Curtis 1959, INAI unpubl. data, MNNHP 1993, McIntosh 1950, Midwestern Ecology Working Group n.d., WNHIP unp

MNNHP 1993, Midwestern Ecology Working Group n.d.

CONHP unpubl. data 2003, Carsey et al. 2003a, Currier 1982, Diamond 1993, Driscoll et al. 1984, Hefley 1937, Jones and Walford 1995, Kittel et al. 1999a, 

CONHP unpubl. data 2003, Carsey et al. 2003a, Driscoll et al. 1984, Girard et al. 1989, Hansen et al. 1990, Johnson et al. 1990a, Johnston 1987, Jones and 

Leahy pers. comm., Midwestern Ecology Working Group n.d., Nelson 1985
Bakowsky 1988, Chapman et al. 1989, Midwestern Ecology Working Group n.d.

INAI unpubl. data, Lauver et al. 1999, Leahy pers. comm., Midwestern Ecology Working Group n.d., Nelson 1985, Steinauer 1989, Steinauer and Rolfsmeier 

Girard 1985, Girard et al. 1989, Johnston 1987, Midwestern Ecology Working Group n.d., NDNHI n.d., Sieg 1991, Wali et al. 1980

Driscoll et al. 1984, Hoffman and Alexander 1987, Johnston 1987, Jones 1992b, McAdams et al. unpubl. data 1998, Midwestern Ecology Working Group n.d

Abrams 1985, Abrams 1986, Abrams 1988, Abrams and Knapp 1986, Bragg and Hulbert 1976, Bragg et al. 1993, Lauver 1989, Lauver et al. 1999, Midweste

Behler 1988, Benyus 1989, Braun 1936, Braun 1950, Bull and Farrand 1977, Clark and Hutchinson 1994, Collingwood and Brush 1984, Craighead 1949, Du

Comer pers. comm., Cowardin et al. 1979, Homoya et al. 1988, Madany 1981, Midwestern Ecology Working Group n.d., White and Madany 1978

Chapman et al. 1989, Homoya et al. 1988, Midwestern Ecology Working Group n.d., White and Madany 1978

Foti pers. comm., Midwestern Ecology Working Group n.d., Nelson 1985, Zollner pers. comm.

Allred and Mitchell 1955, Bruner 1931, Collins and Klahr 1991, Diamond 1993, Ewing et al. 1984, Eyre 1980, Fralish 1987, Fralish 1988b, Fralish et al. 1991, 

Aldrich and Homoya 1986, Campbell and Grubbs 1992, Evans 1991, Fralish 1976, Fralish 1987, Fralish 1988b, Hendricks et al. 1991, Homoya et al. 1988, L

Beals and Cottam 1960, Chambers et al. 1997, Chapman et al. 1989, Epstein pers. comm., MNNHP 1993, Midwestern Ecology Working Group n.d., WNHIP 

Anderson 1996, Braun 1928, Fleming 1999, Fleming and Coulling 2001, Fleming et al. 2001, Fleming pers. comm., Harrison 2004, Kangas 1989, Midwestern 

Curtis 1959, Epstein pers. comm., Kotar and Burger 1996, Midwestern Ecology Working Group n.d., WNHIP unpubl. data

Diamond 1993, Southeastern Ecology Working Group n.d., Turner et al. 1999, Turner et al. unpubl. data

Diamond 1993, Southeastern Ecology Working Group n.d., Turner et al. 1999, Turner et al. unpubl. data

Schafale 2003b, Southeastern Ecology Working Group n.d.

Campbell et al. 1996, Foti 1994a, NatureServe Ecology - Southeastern U.S. unpubl. data, Southeastern Ecology Working Group n.d., Tucker 1989

Allard 1990, Diamond 1993, Southeastern Ecology Working Group n.d.

Allard 1990, Diamond 1993, Gehlbach 1967, Southeastern Ecology Working Group n.d.

Peet et al. unpubl. data 2002, Schafale pers. comm., Southeastern Ecology Working Group n.d.

Allard 1990, Foti 1994a, NatureServe Ecology - Southeastern U.S. unpubl. data, Southeastern Ecology Working Group n.d., Tucker 1989

Evans 1991, Funk 1975, Funk and Fuller 1978, Southeastern Ecology Working Group n.d., TDNH unpubl. data

Allard 1990, Campbell pers. comm., Evans 1991, Southeastern Ecology Working Group n.d., TDNH unpubl. data

Allard 1990, Eyre 1980, Peet et al. unpubl. data 2002, Schafale and Weakley 1990, Southeastern Ecology Working Group n.d.

Areces-Mallea et al. 1999, Dansereau 1966, Southeastern Ecology Working Group n.d.

Allard 1990, Diamond 1993, Southeastern Ecology Working Group n.d.

Allard 1990, Chafin and Jones 1989, Evans 1991, Major et al. 1999, Peet et al. unpubl. data 2002, Pyne 1994, Rawinski 1992, Schafale 1998b, Schafale and 

Allard 1984, Allard 1990, Ambrose 1990a, CAP pers. comm. 1998, Chafin and Jones 1989, Dellinger unpubl. data 1992, Eyre 1980, Fleming and Coulling 20

Fleming and Coulling 2001, Fleming and Moorhead 1996, Fleming et al. 2001, Fleming et al. 2004, Fleming et al. 2007, Young et al. 2006

Dellinger unpubl. data 1992, Eyre 1980, Peet et al. unpubl. data 2002, Schafale 1998b, Schafale 2002, Schafale and Weakley 1990, Schafale pers. comm., S

Fleming and Coulling 2001, Fleming et al. 2001, NatureServe Ecology - Southeastern U.S. unpubl. data, Peet et al. unpubl. data 2002, Southeastern Ecology 

NC Vegetation Survey - Southeast U.S. unpubl. data unpubl. data, Nelson 1986, Peet et al. unpubl. data 2002, Southeastern Ecology Working Group n.d.

NatureServe Ecology - Southeastern U.S. unpubl. data, Schotz pers. comm., Southeastern Ecology Working Group n.d.

Allard 1990, Burns and Honkala 1990a, Burns and Honkala 1990b, Clewell and Ward 1987, Eyre 1980, Frost 1987, Korstian and Brush 1931, Laderman 198

Allard 1990, Clewell and Ward 1987, FNAI 1992a, Oberholster 1993, Schotz pers. comm., Southeastern Ecology Working Group n.d., Wieland 1994b, Wiela

Myers and Ewel 1990, NatureServe Ecology - Southeastern U.S. unpubl. data, Southeastern Ecology Working Group n.d.

Eyre 1980, FNAI 1992a, Oberholster 1993, Schotz pers. comm., Southeastern Ecology Working Group n.d.

Allard 1990, Allard et al. 1990, Clewell 1971, Clewell and Ward 1987, Eyre 1980, FNAI 1992a, Frost and Musselman 1987, Laderman 1989, Landaal 1978, O

Allard 1990, Fleming 1998, Fleming and Moorhead 1998, Fleming et al. 2001, Fleming pers. comm., Peet et al. unpubl. data 2002, Schafale 2000, Schafale a

Hilsenbeck et al. 1979, Southeastern Ecology Working Group n.d., Zane 2004

Southeastern Ecology Working Group n.d., Weakley pers. comm., Wharton et al. 1982

Pyne pers. comm., Schotz pers. comm., Southeastern Ecology Working Group n.d.

Allard 1990, Diamond 1993, Marks and Harcombe 1981, Martin and Smith 1993, McLeod 1975, Nixon et al. 1980a, Smith 1996a, Southeastern Ecology Wor

Smith 1996a, Southeastern Ecology Working Group n.d.

Allard 1990, Batson et al. 1957, Southeastern Ecology Working Group n.d., Whipple et al. 1981

Diamond 1987, Harper 1943, Schotz pers. comm., Southeastern Ecology Working Group n.d.

FNAI 1992b, Southeastern Ecology Working Group n.d.

Allard 1990, Chester et al. 1997, Clark 1974, Clark 1977d, Delcourt and Delcourt 1975, EPA 2004, Evans 1991, Foti 1994b, Foti et al. 1994, Leahy pers. com

Allard 1990, Bridges and Orzell 1989a, Correll and Johnston 1970, Diamond 1993, Kutner and Morse 1996, Little 1979a, Martin and Smith 1991, McLeod 197

Coker 1919, Fleming et al. 2001, Patterson pers. comm., Schafale and Weakley 1990, Small 1933, Southeastern Ecology Working Group n.d.

CAP pers. comm. 1998, Fleming 1993, Fleming and Coulling 2001, Fleming et al. 2001, Fleming et al. 2004, Fleming et al. 2007, Fleming pers. comm., Sout
Allard 1990, Peet et al. unpubl. data 2002, Schafale 2003a, Schafale and Weakley 1990, Southeastern Ecology Working Group n.d.

FNAI 1990, FNAI 1992a, Schotz pers. comm., Southeastern Ecology Working Group n.d.

FNAI 1992a, FNAI 1992b, Southeastern Ecology Working Group n.d.

R. Evans pers. comm., Smith pers. comm., Southeastern Ecology Working Group n.d.

Southeastern Ecology Working Group n.d.

Southeastern Ecology Working Group n.d.

Peet et al. unpubl. data 2002, Southeastern Ecology Working Group n.d., TNC 1998b

Allard 1990, Campbell et al. 1989, Evans 1991, Southeastern Ecology Working Group n.d.

FNAI 1992a, Southeastern Ecology Working Group n.d.

Hoagland 2000, Hopkins 1938, Little 1975, Little 1996, Southeastern Ecology Working Group n.d.

NatureServe Ecology - Southeastern U.S. unpubl. data, Nelson 1985, Southeastern Ecology Working Group n.d.

Hoagland 2000, Hopkins 1938, Leahy pers. comm., Little 1975, Little 1996, Nelson 1985, Nigh pers. comm., Southeastern Ecology Working Group n.d.

Allard 1990, Dorroh 1971, Govus 1998, Krakow 2007, Nelson 1986, Nordman pers. comm., Peet et al. unpubl. data 2002, Southeastern Ecology Working Gr

Leidolf and McDaniel 1998, Schotz pers. comm., Southeastern Ecology Working Group n.d.

Allard 1990, Campbell and Meijer 1989, Evans 1991, Southeastern Ecology Working Group n.d., TDNH unpubl. data

Peet et al. unpubl. data 2002, Southeastern Ecology Working Group n.d.

Southeastern Ecology Working Group n.d.

Allard 1990, Schotz pers. comm., Smith 1996a, Southeastern Ecology Working Group n.d.

Chafin and Shotz 1995, FNAI 1992a, Kindell et al. 1997, Southeastern Ecology Working Group n.d.

Allard 1990, Duever 1984a, FNAI 1992a, FNAI 1992b, Kruer 1992, McGuire and Brown 1974, Ross et al. 1992, Snyder et al. 1990, Southeastern Ecology Wo

Allard 1990, Duever 1984a, FNAI 1992a, FNAI 1992b, Kruer 1992, McGuire and Brown 1974, Ross et al. 1992, Snyder et al. 1990, Southeastern Ecology Wo

Nelson 1986, Peet et al. unpubl. data 2002, Southeastern Ecology Working Group n.d., TNC 1998b

Fleming 1998, Fleming and Moorhead 1998, Fleming et al. 2001, Schafale 2000, Southeastern Ecology Working Group n.d.

Smith 1996a, Southeastern Ecology Working Group n.d.

NCNHP unpubl. data, Peet et al. unpubl. data 2002, Schafale 2000, Schafale and Weakley 1990, Schafale pers. comm., Southeastern Ecology Working Gro

NatureServe Ecology - Southeastern U.S. unpubl. data, Schotz pers. comm., Southeastern Ecology Working Group n.d., Wieland 2000b

FNAI 1990, FNAI 1992a, FNAI 1992b, Southeastern Ecology Working Group n.d.

FNAI 1990, FNAI 1992a, FNAI 1992b, Southeastern Ecology Working Group n.d.

Allard 1990, FNAI 1992a, Schotz pers. comm., Southeastern Ecology Working Group n.d.

Allard 1990, Southeastern Ecology Working Group n.d.

Allard 1990, Southeastern Ecology Working Group n.d.

Adams and Stephenson 1991, Allard 1990, Anderson et al. 1990, Belden et al. 1994, Brown 1941, Bruck 1988, Busing et al. 1988, Cogbill and White 1991, C

Allard 1990, Golden 1974, Golden 1981, Livingston and Mitchell 1976, McLeod pers. comm., NatureServe Ecology - Southeastern U.S. unpubl. data, Peet et 

Allard 1990, Allard and Leonard 1952, Anderson et al. 1990, CAP pers. comm. 1998, Clarkson 1964, Cogbill and White 1991, Crandall 1958, Eyre 1980, Gol

Adams and Stephenson 1991, Allard and Leonard 1952, Bailey and Ware 1990, Clarkson 1964, Eyre 1980, Fleming and Coulling 2001, Fleming and Moorhe

Diamond 1993, Southeastern Ecology Working Group n.d.

Diamond 1993, Southeastern Ecology Working Group n.d.

Diamond 1993, Southeastern Ecology Working Group n.d.

Diamond 1993, Southeastern Ecology Working Group n.d.

Diamond 1993, Southeastern Ecology Working Group n.d.

Diamond 1993, Southeastern Ecology Working Group n.d.

FNAI 1992a, FNAI 1992b, Southeastern Ecology Working Group n.d.

Allard 1990, FNAI 1992a, Johnson and Barbour 1990, Schotz pers. comm., Southeastern Ecology Working Group n.d.

Allard 1990, FNAI 1992a, Heuberger et al. 1997, Myers 1990, NatureServe Ecology - Southeastern U.S. unpubl. data, Southeastern Ecology Working Group 

NatureServe Ecology - Southeastern U.S. unpubl. data, Southeastern Ecology Working Group n.d.

Cain and Shelton 1994, Foti pers. comm., Halls and Homesley 1966, NatureServe Ecology - Southeastern U.S. unpubl. data, R. Evans pers. comm., Schotz 

Allard 1990, Allred and Mitchell 1955, Diamond 1993, Eyre 1980, Ferguson 1958, Garren 1943, Hatchell 1964, Landers 1989, Martin and Smith 1991, Martin 

Govus 2003, Schotz pers. comm., Southeastern Ecology Working Group n.d.

NatureServe Ecology - Southeastern U.S. unpubl. data, Southeastern Ecology Working Group n.d., Turner et al. unpubl. data

NatureServe Ecology - Southeastern U.S. unpubl. data, Peet et al. unpubl. data 2002, Schafale and Weakley 1990, Southeastern Ecology Working Group n.

Fleming and Coulling 2001, Fleming et al. 2001, Southeastern Ecology Working Group n.d., VDNH 2003

Bruner 1931, Cantwell 1981, Duck and Fletcher 1945, Eyre 1980, Hoagland 2000, Johnson 1986b, Kennedy 1973, Masters et al. 1995, Nelson 1985, Osborn 
Allard 1990, Diamond 1993, Egan 1987, Eyre 1980, Foti pers. comm., Hoagland pers. comm., Martin and Smith 1991, Martin and Smith 1993, Martin et al. 1

Schotz pers. comm., Southeastern Ecology Working Group n.d.

Abrahamson et al. 1984, FNAI 1992a, Southeastern Ecology Working Group n.d.

FNAI 1992a, FNAI 1992b, Southeastern Ecology Working Group n.d.

FNAI 1992a, FNAI 1992b, Southeastern Ecology Working Group n.d.

Peet et al. unpubl. data 2002, Schotz pers. comm., Smith pers. comm., Southeastern Ecology Working Group n.d.

Schotz pers. comm., Southeastern Ecology Working Group n.d.

Schotz pers. comm., Smith 1996a, Southeastern Ecology Working Group n.d.

Southeastern Ecology Working Group n.d.

Schotz pers. comm., Smith 1996a, Smith 1996b, Southeastern Ecology Working Group n.d.

Clewell 1981, Schotz pers. comm., Southeastern Ecology Working Group n.d., Weakley pers. comm.

Southeastern Ecology Working Group n.d.

Huffman and Judd 1998, Southeastern Ecology Working Group n.d.

Southeastern Ecology Working Group n.d.

Fleming et al. 2001, Frost and Musselman 1987, Schafale 1994, Schafale 2000, Schafale 2003b, Schafale and Weakley 1990, Southeastern Ecology Workin

Diamond 1993, Southeastern Ecology Working Group n.d., Turner et al. unpubl. data

NatureServe Ecology - Southeastern U.S. unpubl. data, Southeastern Ecology Working Group n.d.

Allard 1990, Golden 1979, NC Vegetation Survey - Southeast U.S. unpubl. data unpubl. data, NatureServe Ecology - Southeastern U.S. unpubl. data, Peet e

Southeastern Ecology Working Group n.d.

Glitzenstein and Streng 2004, NC Vegetation Survey - Southeast U.S. unpubl. data unpubl. data, Peet 1996, Peet et al. unpubl. data 2002, Schafale 1994, S

Peet 1996, Peet et al. unpubl. data 2002, Schafale 2000, Schafale 2003b, Schafale and Weakley 1990, Southeastern Ecology Working Group n.d., Wentwor

Bridges and Orzell 1989a, Evans 1997, Southeastern Ecology Working Group n.d., Turner et al. unpubl. data

Schafale 1994, Schafale 2000, Schafale 2003b, Schafale and Weakley 1990, Southeastern Ecology Working Group n.d.

Schafale 1994, Schafale 2000, Schafale 2003b, Schafale and Weakley 1990, Southeastern Ecology Working Group n.d.

Allard 1990, Bridges and Orzell 1989a, Correll and Johnston 1970, Diamond 1993, Dickson et al. 1993, Eyre 1980, Hatchell 1964, Martin and Smith 1991, M

Schafale 1994, Schafale 2000, Schafale 2003b, Schafale and Weakley 1990, Southeastern Ecology Working Group n.d.

Carr unpubl. data, Clewell 1971, Collins et al. 2001, NatureServe Ecology - Southeastern U.S. unpubl. data, Southeastern Ecology Working Group n.d.

Heuberger et al. 1997, Kalisz 1982, NatureServe Ecology - Southeastern U.S. unpubl. data, Southeastern Ecology Working Group n.d.

Allard 1990, Bridges and Orzell 1989a, Correll and Johnston 1970, Diamond 1993, Egan 1987, Eyre 1980, Martin and Smith 1991, Orzell 1990, Smith 1996a

Southeastern Ecology Working Group n.d.

Peet et al. unpubl. data 2002, Southeastern Ecology Working Group n.d.

Schafale 1994, Schafale 2000, Schafale 2003b, Schafale and Weakley 1990, Southeastern Ecology Working Group n.d.

Allard 1990, Diamond 1993, Smith 1996a, Southeastern Ecology Working Group n.d., Turner et al. 1999, Turner et al. unpubl. data

Southeastern Ecology Working Group n.d.

Allard 1990, Peet 1996, Schafale 1994, Schafale 2000, Schafale 2003b, Schafale and Weakley 1990, Southeastern Ecology Working Group n.d.

NatureServe Ecology - Southeastern U.S. unpubl. data, Southeastern Ecology Working Group n.d.

Allard 1990, Schafale 1994, Schafale 2000, Schafale 2003b, Schafale and Weakley 1990, Southeastern Ecology Working Group n.d.

Allard 1990, Schafale 1994, Schafale 2000, Schafale 2003b, Schafale and Weakley 1990, Southeastern Ecology Working Group n.d.

Peet et al. unpubl. data 2002, Southeastern Ecology Working Group n.d.

Allard 1990, Allen 1956, FNAI 1992a, FNAI 1992b, NatureServe Ecology - Southeastern U.S. unpubl. data, Orzell pers. comm., Peet and Allard 1993, Pessin 

Southeastern Ecology Working Group n.d.

Allard 1990, Moore pers. comm., Peet and Allard 1993, Southeastern Ecology Working Group n.d., Wieland 1994b, Wieland 2000b

Glitzenstein and Streng 2004, Peet 1996, Southeastern Ecology Working Group n.d.

Southeastern Ecology Working Group n.d.

Schafale 1994, Schafale 2000, Schafale 2003b, Schafale and Weakley 1990, Southeastern Ecology Working Group n.d.

Allard 1990, Diamond 1993, Evans 1996, Eyre 1980, Hatchell 1964, Haywood and Thill 1995, Kilpatrick et al. 1986, Martin et al. 1993, NatureServe Ecology 

Allard 1990, Evans 1996, Eyre 1980, NatureServe Ecology - Southeastern U.S. unpubl. data, Smith 1996a, Southeastern Ecology Working Group n.d., Turne

Moore pers. comm., Peet and Allard 1993, Schotz pers. comm., Southeastern Ecology Working Group n.d., Wieland 1994b, Wieland 2000b

Schafale 1994, Schafale 2000, Schafale 2003b, Schafale and Weakley 1990, Southeastern Ecology Working Group n.d.

Glitzenstein and Streng 2004, Peet 1996, Southeastern Ecology Working Group n.d.

McGee pers. comm., Southeastern Ecology Working Group n.d.

Bridges 1988, Diamond 1993, Smith 1996a, Smith pers. comm., Southeastern Ecology Working Group n.d.
Southeastern Ecology Working Group n.d.

Allard 1990, Bridges and Orzell 1989a, Correll and Johnston 1970, Diamond 1993, Eyre 1980, Hatchell 1964, Martin and Smith 1991, Martin and Smith 1993

Southeastern Ecology Working Group n.d.

Allard 1990, Bridges and Orzell 1989a, Correll and Johnston 1970, Diamond 1993, Eyre 1980, Hatchell 1964, Martin and Smith 1991, Martin and Smith 1993

Diamond 1993, Smith 1996a, Southeastern Ecology Working Group n.d.

FNAI 1992a, NatureServe Ecology - Southeastern U.S. unpubl. data, Schotz pers. comm., Southeastern Ecology Working Group n.d.

Lemon 1949, NatureServe Ecology - Southeastern U.S. unpubl. data, Peet 1996, Peet et al. unpubl. data 2002, Southeastern Ecology Working Group n.d.

Allard 1990, Diamond 1993, Southeastern Ecology Working Group n.d.

Diamond 1993, Eyre 1980, Southeastern Ecology Working Group n.d.

Diamond 1993, Eyre 1980, Southeastern Ecology Working Group n.d.

Peet et al. unpubl. data 2002, Schafale 1998b, Schafale pers. comm., Southeastern Ecology Working Group n.d., TDNH unpubl. data

Evans 1991, Southeastern Ecology Working Group n.d.

Schafale 2000, Schafale and Weakley 1990, Southeastern Ecology Working Group n.d.

NatureServe Ecology - Southeastern U.S. unpubl. data, Southeastern Ecology Working Group n.d.

Allard 1990, Fleming and Moorhead 1998, Fleming et al. 2001, Fleming pers. comm., Schafale 2000, Schafale and Weakley 1990, Southeastern Ecology Wo

Fleming et al. 2001, Frost et al. 1990, Schafale 2000, Schafale 2003b, Schafale and Weakley 1990, Schafale pers. comm., Southeastern Ecology Working G

FNAI 1990, FNAI 1992b, NatureServe Ecology - Southeastern U.S. unpubl. data, Southeastern Ecology Working Group n.d.

Allard 1990, DeYoung 1979, Govus 1982, NatureServe Ecology - Southeastern U.S. unpubl. data, Patterson 1994, Peet et al. unpubl. data 2002, Pyne 1994

Allard 1990, Diamond 1993, Dickson et al. 1993, Eyre 1980, Hatchell 1964, Martin and Smith 1991, Martin and Smith 1993, Smith 1988a, Smith 1996a, Smit

Schafale 2000, Schafale and Weakley 1990, Schafale pers. comm., Southeastern Ecology Working Group n.d.

Bowman 1999, Coulling unpubl. data 2007, Fleming 1998, Fleming and Moorhead 1998, Fleming et al. 2001, Harrison 2004, Southeastern Ecology Working 

Schafale and Weakley 1990, Southeastern Ecology Working Group n.d.

Eyre 1980, Schafale 2000, Schafale and Weakley 1990, Southeastern Ecology Working Group n.d.

Allard 1990, Peet et al. unpubl. data 2002, Schafale 1998b, Schafale 2002, Southeastern Ecology Working Group n.d., TDNH unpubl. data

Allard 1990, McLeod 1988, NatureServe Ecology - Southeastern U.S. unpubl. data, Newell and Peet 1995, Newell et al. 1997, Peet et al. unpubl. data 2002, 

Southeastern Ecology Working Group n.d.

Diamond 1993, Southeastern Ecology Working Group n.d.

Allard 1990, Pyne 1994, Pyne 2000, Southeastern Ecology Working Group n.d., TDNH unpubl. data, TNC 1998a

Govus 1999, Schotz pers. comm., Southeastern Ecology Working Group n.d.

Fleming et al. 2001, Fleming pers. comm., J. Harrison pers. comm., Southeastern Ecology Working Group n.d., VDNH 2003

NatureServe Ecology - Southeastern U.S. unpubl. data, Peet et al. unpubl. data 2002, Schafale and Weakley 1990, Southeastern Ecology Working Group n.

NatureServe Ecology - Southeastern U.S. unpubl. data, Peet et al. unpubl. data 2002, Schafale 1998b, Southeastern Ecology Working Group n.d., TDNH un

NatureServe Ecology - Southeastern U.S. unpubl. data, Southeastern Ecology Working Group n.d.

Peet et al. unpubl. data 2002, Schafale and Weakley 1990, Schafale pers. comm., Southeastern Ecology Working Group n.d.

Peet et al. unpubl. data 2002, Schafale and Weakley 1990, Schotz pers. comm., Southeastern Ecology Working Group n.d.

Keith 2003, NatureServe Ecology - Southeastern U.S. unpubl. data, R. Evans pers. comm., Southeastern Ecology Working Group n.d.

Allard 1990, McCormick and Platt 1980, Newell and Peet 1995, Patterson 1994, Peet et al. unpubl. data 2002, Schafale 1998b, Schafale and Weakley 1990, 

Allard 1990, Foti 1994b, Foti and Pell 1986, Foti et al. 1994, Foti pers. comm., MacRoberts and MacRoberts 1997a, Pell 1983, Pell 1984, Roberts 1978, Smi

Barker and Jameson 1975, Dale 1965, Hoagland 2000, Southeastern Ecology Working Group n.d.

Peet et al. unpubl. data 2002, Schafale 1994, Schafale and Weakley 1990, Schafale pers. comm., Southeastern Ecology Working Group n.d.

Southeastern Ecology Working Group n.d., TDNH unpubl. data, Wharton 1945

Allard 1990, Hoagland 1997, Hoagland 2000, Southeastern Ecology Working Group n.d., Zanoni et al. 1979

Diamond 1993, McAlister and McAlister 1995, Nixon and Muller 1997, Southeastern Ecology Working Group n.d.

FNAI 1992a, FNAI 1992b, Johnson et al. 1990b, Southeastern Ecology Working Group n.d.

FNAI 1992a, FNAI 1992b, Southeastern Ecology Working Group n.d.

FNAI 1992a, Johnson pers. comm., Schotz pers. comm., Southeastern Ecology Working Group n.d.

FNAI 1992a, FNAI 1992b, Schotz pers. comm., Southeastern Ecology Working Group n.d.

FNAI 1992a, FNAI 1992b, NatureServe Ecology - Southeastern U.S. unpubl. data, Southeastern Ecology Working Group n.d.

FNAI 1992a, Johnson pers. comm., Kindell et al. 1997, Southeastern Ecology Working Group n.d.

Southeastern Ecology Working Group n.d.

Southeastern Ecology Working Group n.d.

Allard 1990, Diamond 1993, Diamond et al. 1992, Orzell 1990, Riskind and Diamond 1988, Southeastern Ecology Working Group n.d.
Allard 1990, Schotz pers. comm., Southeastern Ecology Working Group n.d.

Allard 1990, Schafale 2000, Schafale and Weakley 1990, Southeastern Ecology Working Group n.d.

Chester and Ellis 1989, Ellis and Chester 1989, Evans 1991, Southeastern Ecology Working Group n.d., TDNH unpubl. data

Foti 1994b, Foti et al. 1994, Foti pers. comm., Heineke 1987, Saucier 1978, Southeastern Ecology Working Group n.d., Zollner pers. comm.

Smith 1996a, Southeastern Ecology Working Group n.d.

Nelson 1985, Southeastern Ecology Working Group n.d.

Allard 1990, DeSelm 1988, Southeastern Ecology Working Group n.d., TDNH unpubl. data

Smith 1996a, Southeastern Ecology Working Group n.d.

Allard 1990, Fleming 1998, Fleming and Moorhead 1998, Fleming et al. 2001, Fleming pers. comm., Schafale 2000, Schafale and Weakley 1990, Southeast

Peet et al. unpubl. data 2002, Southeastern Ecology Working Group n.d., TNC 1998b

Southeastern Ecology Working Group n.d.

Southeastern Ecology Working Group n.d.

Diamond 1993, Diggs et al. 1999, Southeastern Ecology Working Group n.d.

Southeastern Ecology Working Group n.d.

Glitzenstein and Streng 2004, Southeastern Ecology Working Group n.d.

Smith 1996a, Southeastern Ecology Working Group n.d.

Southeastern Ecology Working Group n.d.

Fleming et al. 2001, LeGrand 1999, Schafale and Weakley 1990, Southeastern Ecology Working Group n.d.

Fleming 2002b, Fleming and Patterson 2004, Fleming and Weber 2003, Fleming et al. 2001, Southeastern Ecology Working Group n.d., VDNH 2003

Orzell et al. 1985, Southeastern Ecology Working Group n.d.

Pyne 1994, Pyne 2000, Southeastern Ecology Working Group n.d., TDNH unpubl. data, TNC 1998a

Diamond 1993, Southeastern Ecology Working Group n.d., Turner et al. 1999, Turner et al. unpubl. data, Watson 1979

ALNHP 2002, Fleming et al. 2001, Fleming pers. comm., Patterson pers. comm., Peet et al. unpubl. data 2002, Schafale and Weakley 1990, Schotz pers. co

NC Vegetation Survey - Southeast U.S. unpubl. data unpubl. data, NatureServe Ecology - Southeastern U.S. unpubl. data, Peet et al. unpubl. data 2002, Sch

Evans 1991, Southeastern Ecology Working Group n.d., TDNH unpubl. data

Allard 1990, CAP pers. comm. 1998, Coker and Totten 1945, DeLapp 1978, Eyre 1980, Fernald 1950, Fleming et al. 2001, Golden 1974, Kartesz 1999, McD

Allard 1990, Peet et al. unpubl. data 2002, Schafale 1998b, Schafale pers. comm., Southeastern Ecology Working Group n.d., TDNH unpubl. data

NatureServe Ecology - Southeastern U.S. unpubl. data, Schotz pers. comm., Southeastern Ecology Working Group n.d., TDNH unpubl. data

Allard 1990, Pyne 1994, Pyne 2000, Southeastern Ecology Working Group n.d., TDNH unpubl. data, TNC 1998a

Fleming et al. 2001, Oakley et al. 1995, Peet et al. unpubl. data 2002, Schafale and Weakley 1990, Southeastern Ecology Working Group n.d.

Fleming et al. 2001, Oakley et al. 1995, Patterson pers. comm., Peet and Christensen 1980, Schafale 2003a, Schafale and Weakley 1990, Southeastern Eco

Oakley et al. 1995, Peet et al. unpubl. data 2002, Schafale 2003a, Schafale and Weakley 1990, Southeastern Ecology Working Group n.d.

NatureServe Ecology - Southeastern U.S. unpubl. data, Southeastern Ecology Working Group n.d.

Eyre 1980, Foti 1994b, Foti et al. 1994, NatureServe Ecology - Southeastern U.S. unpubl. data, Southeastern Ecology Working Group n.d., Tucker 1989

Leidolf and McDaniel 1998, Lowe 1921, Mohr 1901, Schotz pers. comm., Southeastern Ecology Working Group n.d.

Arkansas Geological Commission 2001, Babcock et al. 2001, Campbell pers. comm., Foti 1994b, Foti et al. 1994, Southeastern Ecology Working Group n.d

Allard 1990, Pyne 1994, Southeastern Ecology Working Group n.d., TDNH unpubl. data

Allard 1990, Braun 1950, Frick 1939, Pyne 1994, Pyne 1997, Schotz pers. comm., Southeastern Ecology Working Group n.d., TDNH unpubl. data

Allard 1990, Diamond 1993, Southeastern Ecology Working Group n.d.

Allard 1990, Dorroh 1971, Eleuterius and Otvos 1979, NatureServe Ecology - Southeastern U.S. unpubl. data, Schotz pers. comm., Smith pers. comm., Sout

Allard 1990, Ambrose 1990a, Aulbach-Smith 1984, Bozeman 1975, E. Harrison pers. comm., EPA 2004, FNAI 1992a, Gaddy 1981, Godfrey 1976, Hardin 19

Allard 1990, Diamond 1993, Diamond et al. 1992, Southeastern Ecology Working Group n.d.

Diamond 1993, Smith 1999, Southeastern Ecology Working Group n.d.

FNAI 1990, FNAI 1992b, Johnson et al. 1992a, Kindell et al. 1997, Patterson et al. 1994, Southeastern Ecology Working Group n.d.

Allard 1990, LeGrand et al. 1992, Schafale and Weakley 1990, Schafale pers. comm., Southeastern Ecology Working Group n.d., Wentworth et al. 1993

Allard 1990, Ambrose 1990a, Bellis 1992, Bourdeau and Oosting 1959, Clampitt 1991, EPA 2004, Fleming et al. 2001, Keys et al. 1995, Schafale and Weak

Southeastern Ecology Working Group n.d.

Diamond 1993, Southeastern Ecology Working Group n.d.

Southeastern Ecology Working Group n.d.

Southeastern Ecology Working Group n.d.

FNAI 1992a, FNAI 1992b, Peet et al. unpubl. data 2002, Schotz pers. comm., Southeastern Ecology Working Group n.d.

Allard 1990, Ross et al. 1992, Southeastern Ecology Working Group n.d.
Hilsenbeck et al. 1979, Southeastern Ecology Working Group n.d.

Allard 1990, Clover 1937, Diamond 1993, Diamond et al. 1992, Jahrsdoerfer and Leslie 1988, Southeastern Ecology Working Group n.d., Wynd 1944

EPA 2004, Govus 1998, Keys et al. 1995, Peet et al. unpubl. data 2002, Southeastern Ecology Working Group n.d.

Ewel 1990b, FNAI 1992b, NatureServe Ecology - Southeastern U.S. unpubl. data, Southeastern Ecology Working Group n.d., Vince et al. 1989

Ewel 1990b, FNAI 1992b, Southeastern Ecology Working Group n.d., Vince et al. 1989

FNAI 1992a, Gunderson and Loftus 1993, Hilsenbeck et al. 1979, Olmsted et al. 1980a, Southeastern Ecology Working Group n.d.

Southeastern Ecology Working Group n.d.

Schafale 2003b, Schafale and Weakley 1990, Southeastern Ecology Working Group n.d.

Southeastern Ecology Working Group n.d.

Allard 1990, Boles and Dick-Peddie 1983, Diamond 1993, Diamond et al. 1992, Southeastern Ecology Working Group n.d.

FNAI 1992b, Kindell pers. comm., Schotz pers. comm., Southeastern Ecology Working Group n.d.

FNAI 1992a, FNAI 1992b, Hilsenbeck et al. 1979, Southeastern Ecology Working Group n.d.

FNAI 1992a, FNAI 1992b, Hilsenbeck et al. 1979, Monk and Brown 1965, Olmsted et al. 1980a, Southeastern Ecology Working Group n.d.

Glitzenstein and Streng 2004, Southeastern Ecology Working Group n.d.

FNAI 1992a, FNAI 1992b, Hilsenbeck et al. 1979, Olmsted et al. 1980a, Southeastern Ecology Working Group n.d.

Schafale 2000, Schafale 2003b, Schafale and Weakley 1990, Southeastern Ecology Working Group n.d.

Schafale 2000, Schafale 2003b, Schafale and Weakley 1990, Southeastern Ecology Working Group n.d.

Gunderson and Loope 1982a, Hilsenbeck et al. 1979, Southeastern Ecology Working Group n.d.

Gunderson and Loope 1982a, Hilsenbeck et al. 1979, Southeastern Ecology Working Group n.d.

Bennett and Nelson 1991, Carter 1978, NatureServe Ecology - Southeastern U.S. unpubl. data, Nifong 1982, Peroni 1988, Schafale 2000, Schafale and Wea

FNAI 1990, FNAI 1992a, FNAI 1992b, Schotz pers. comm., Southeastern Ecology Working Group n.d.

FNAI 1992a, NatureServe Ecology - Southeastern U.S. unpubl. data, Southeastern Ecology Working Group n.d.

FNAI 1990, FNAI 1992a, FNAI 1992b, Southeastern Ecology Working Group n.d.

Fleming 1998, Fleming and Moorhead 1998, Fleming et al. 2001, Schafale 2000, Schafale and Weakley 1990, Southeastern Ecology Working Group n.d., VD

Allard 1990, Diamond 1993, Diamond et al. 1992, Ford and Van Auken 1982, Riskind and Diamond n.d., Southeastern Ecology Working Group n.d.

Southeastern Ecology Working Group n.d.

Coulling 2002, Fleming pers. comm., Harrison et al. 2004, Southeastern Ecology Working Group n.d.

Eyre 1980, Southeastern Ecology Working Group n.d.

Schafale and Weakley 1990, Schafale pers. comm., Southeastern Ecology Working Group n.d.

NatureServe Ecology - Southeastern U.S. unpubl. data, Schotz pers. comm., Southeastern Ecology Working Group n.d.

Major et al. 1999, Peet et al. unpubl. data 2002, Schafale 1998b, Schafale and Weakley 1990, Southeastern Ecology Working Group n.d., TDNH unpubl. dat

Allard 1990, CAP pers. comm. 1998, Evans 1991, Eyre 1980, Fike 1999, Fleming and Coulling 2001, Fleming et al. 2001, Peet et al. unpubl. data 2002, Scha

Eyre 1980, Fike 1999, Fleming and Coulling 2001, Fleming and Moorhead 1996, Fleming et al. 2001, Fleming et al. 2004, Rawinski et al. 1994, Rawinski et a

Golden 1974, Newell et al. 1997, Peet et al. unpubl. data 2002, Schafale 1998b, Schafale and Weakley 1990, Schafale pers. comm., Southeastern Ecology W

Allard 1990, NatureServe Ecology - Southeastern U.S. unpubl. data, Peet et al. unpubl. data 2002, Schafale 1998b, Schafale and Weakley 1990, Southeaste

Allard 1990, Fleming and Coulling 2001, Fleming et al. 2001, Fleming et al. 2004, Peet et al. unpubl. data 2002, Rentch et al. 2000, Schafale 1998b, Schafal

Diamond 1993, Southeastern Ecology Working Group n.d., Turner et al. 1997

Atzet and McCrimmon 1990, Bourgeron and Engelking 1994, Driscoll et al. 1984, Kagan et al. 2004, Western Ecology Working Group n.d.

Atzet and Wheeler 1984, Atzet et al. 1996, Bourgeron and Engelking 1994, Driscoll et al. 1984, Hawk 1977, Jimerson 1994, Kagan et al. 2000, Western Eco

Atzet et al. 1996, Bourgeron and Engelking 1994, Driscoll et al. 1984, Hawk 1977, Kagan et al. 2000, Thilenius 1968, Western Ecology Working Group n.d., Z

Atzet and Wheeler 1984, Atzet et al. 1996, Bourgeron and Engelking 1994, Driscoll et al. 1984, Kagan et al. 2000, Western Ecology Working Group n.d.

Atzet and Wheeler 1984, Atzet et al. 1996, Bourgeron and Engelking 1994, Driscoll et al. 1984, Kagan et al. 2000, Western Ecology Working Group n.d.

Atzet and Wheeler 1984, Bourgeron and Engelking 1994, Driscoll et al. 1984, Kagan et al. 2000, Western Ecology Working Group n.d.

Baker 1986, Baker 1989a, Baker 1989b, Bourgeron and Engelking 1994, CONHP unpubl. data 2003, Carsey et al. 2003a, Driscoll et al. 1984, Kittel et al. 199

Bourgeron and Engelking 1994, Driscoll et al. 1984, Hopkins 1979a, Kagan et al. 2000, Western Ecology Working Group n.d.

Bourgeron and Engelking 1994, Driscoll et al. 1984, Hopkins 1979a, Kagan et al. 2000, Western Ecology Working Group n.d.

Bourgeron and Engelking 1994, CONHP unpubl. data 2003, Driscoll et al. 1984, Hess 1981, Hess and Alexander 1986, Johnston 1987, Muldavin et al. 2006, 

Bourgeron and Engelking 1994, DeVelice and Ludwig 1983b, Dick-Peddie 1993, Driscoll et al. 1984, Moir and Ludwig 1979, Muldavin et al. 1986, Muldavin e

Alexander et al. 1984a, Bourgeron and Engelking 1994, Driscoll et al. 1984, Fitzhugh et al. 1987, Muldavin et al. 1986, Muldavin et al. 1996, Stuever and Hay

Bourgeron and Engelking 1994, Driscoll et al. 1984, Kagan et al. 2000, Topik et al. 1988, Western Ecology Working Group n.d.

Bourgeron and Engelking 1994, Kagan et al. 2000, Topik 1989, Topik et al. 1988, Western Ecology Working Group n.d.

Bourgeron and Engelking 1994, Driscoll et al. 1984, Kagan et al. 2000, Topik et al. 1988, Western Ecology Working Group n.d.
Bourgeron and Engelking 1994, Driscoll et al. 1984, Kagan 1987c, Kagan et al. 2000, Parker 1982, Western Ecology Working Group n.d.

Bourgeron and Engelking 1994, Driscoll et al. 1984, John and Tart 1986, Lillybridge et al. 1995, Topik 1989, Topik et al. 1988, Western Ecology Working Gro

Bourgeron and Engelking 1994, Cooper et al. 1987, Driscoll et al. 1984, Fischer and Bradley 1987, Johnson and Simon 1985, Johnson and Simon 1987, Kag

Bourgeron and Engelking 1994, Cooper et al. 1985, Driscoll et al. 1984, Johnson and Simon 1987, Kagan et al. 2000, Steele et al. 1981, Topik 1989, Topik e

Bourgeron and Engelking 1994, Clausnitzer 1993, Cooper et al. 1987, Driscoll et al. 1984, Hall 1973, Johnson and Clausnitzer 1992, Johnson and Simon 198

Antos 1977, Bourgeron and Engelking 1994, Clausnitzer 1993, Clausnitzer and Zamora 1987, Cooper et al. 1987, Crawford and Johnson 1985, Crowe and C

Bourgeron and Engelking 1994, Cooper et al. 1987, Driscoll et al. 1984, Pfister et al. 1977, Steele et al. 1981, UNESCO 1973, Western Ecology Working Gro

Bourgeron and Engelking 1994, Driscoll et al. 1984, Topik 1989, WNHP unpubl. data, Western Ecology Working Group n.d.

Bourgeron and Engelking 1994, Driscoll et al. 1984, Henderson et al. 1986, Henderson et al. 1989, Western Ecology Working Group n.d.

Bassett et al. 1987, Bourgeron and Engelking 1994, DeVelice and Ludwig 1983b, Dick-Peddie 1993, Driscoll et al. 1984, Moir and Ludwig 1979, Muldavin et 

Chappell 2001, Kagan et al. 2000, WNHP unpubl. data, Western Ecology Working Group n.d.

Baker 1984a, Baker 1989a, Bourgeron and Engelking 1994, Boyce 1977, CONHP unpubl. data 2003, Carsey et al. 2003a, Driscoll et al. 1984, Kittel and Led

Bourgeron and Engelking 1994, Driscoll et al. 1984, IDCDC 2005, Padgett et al. 1989, Western Ecology Working Group n.d.

Bourgeron and Engelking 1994, Driscoll et al. 1984, IDCDC 2005, Miller 1976, Western Ecology Working Group n.d.

Bourgeron and Engelking 1994, Driscoll et al. 1984, Miller 1976, Western Ecology Working Group n.d.

Bourgeron and Engelking 1994, CONHP unpubl. data 2003, Daubenmire 1970, Driscoll et al. 1984, Johnson and Simon 1987, Johnston 1987, Kagan et al. 2

Bourgeron and Engelking 1994, Dealy 1975, Dealy et al. 1981, Driscoll et al. 1984, Johnson and Clausnitzer 1992, Kagan et al. 2000, Western Ecology Work

Bourgeron and Engelking 1994, Dealy 1975, Driscoll et al. 1984, Gruell et al. 1985, Kagan et al. 2000, Western Ecology Working Group n.d.

Atzet and Wheeler 1984, Atzet et al. 1996, Bourgeron and Engelking 1994, Driscoll et al. 1984, Hawk 1977, Jimerson 1994, Kagan et al. 2000, Western Eco

Atzet et al. 1996, Becking 1982, Bourgeron and Engelking 1994, Copeland unpubl. data 1978, Driscoll et al. 1984, Hawk 1977, Jimerson 1994, Kagan 1987c

Bassett et al. 1987, Bourgeron and Engelking 1994, Brown 1982, Carmichael et al. 1978, Driscoll et al. 1984, Niering and Lowe 1984, Parker 1980a, Parker 1

Bassett et al. 1987, Bourgeron and Engelking 1994, Brown 1982, Carmichael et al. 1978, Driscoll et al. 1984, Larson and Moir 1986, NMNHP unpubl. data, U

Cheatham and Haller 1975, Griffin and Critchfield 1972, Keeler-Wolf 1990, Sawyer and Keeler-Wolf 1995, Vogl et al. 1988, Western Ecology Working Group 

Cheatham and Haller 1975, Griffin and Critchfield 1972, Keeler-Wolf 1990, Sawyer and Keeler-Wolf 1995, Vogl et al. 1988, Western Ecology Working Group 

Kagan et al. 2000, Western Ecology Working Group n.d.

Kagan et al. 2000, Western Ecology Working Group n.d.

Muldavin et al. 2000a, NMNHP unpubl. data, Western Ecology Working Group n.d.

Kagan et al. 2004, ORNHP unpubl. data, Western Ecology Working Group n.d., Youtie and Winward 1977

Bourgeron and Engelking 1994, Dealy 1975, Dealy et al. 1981, Driscoll et al. 1984, Kagan et al. 2000, Western Ecology Working Group n.d.

Bourgeron and Engelking 1994, CONHP unpubl. data 2003, Driscoll et al. 1984, Warren n.d., Western Ecology Working Group n.d.

Bourgeron and Engelking 1994, Driscoll et al. 1984, Moir and Carleton 1987, USFS 1985c, Western Ecology Working Group n.d.

Bourgeron and Engelking 1994, DeVelice and Lesica 1993, Driscoll et al. 1984, Lesica and DeVelice 1992, MTNHP 2002b, Western Ecology Working Group 

Bourgeron and Engelking 1994, CONHP unpubl. data, CONHP unpubl. data 2003, Driscoll et al. 1984, Hess 1981, Hess and Alexander 1986, Johnston 1987

Bourgeron and Engelking 1994, CONHP unpubl. data 2003, Driscoll et al. 1984, Hess 1981, Hess and Alexander 1986, Johnston 1987, Wasser and Hess 19

Badaracco 1971, Bourgeron and Engelking 1994, CONHP unpubl. data 2003, Driscoll et al. 1984, Goodding 1923, Moran 1981, Ramaley 1909, Wells 1965, 

Achuff et al. 2002a, Arno and Habeck 1972, Pfister et al. 1977, Western Ecology Working Group n.d., Williams and Smith 1990

Arno 1970, Arno and Habeck 1972, Bourgeron and Engelking 1994, Driscoll et al. 1984, Lillybridge et al. 1995, MTNHP 2002b, Western Ecology Working Gr

Western Ecology Working Group n.d.

Bourgeron and Engelking 1994, Driscoll et al. 1984, Hansen et al. 1995, IDCDC 2005, MTNHP 2002b, Moseley et al. 1991, Steele et al. 1981, Steele et al. 1

Bailey 1995, Bourgeron and Engelking 1994, Driscoll et al. 1984, Hansen et al. 1991, Hansen et al. 1995, MTNHP 2002b, UNESCO 1973, Western Ecology 

Alexander et al. 1984a, Bourgeron and Engelking 1994, Driscoll et al. 1984, Moir and Ludwig 1979, Muldavin et al. 1996, Western Ecology Working Group n.

Bourgeron and Engelking 1994, Cooper et al. 1999, Crowe and Clausnitzer 1997, Crowe et al. 2004, Dorn 1992, Driscoll et al. 1984, IDCDC 2005, Johnston 

Bourgeron and Engelking 1994, Driscoll et al. 1984, Fitzhugh et al. 1987, Larson and Moir 1986, Moir and Ludwig 1979, Stuever and Hayden 1997b, Western 

Baker 1984a, Bourgeron and Engelking 1994, CONHP unpubl. data 2003, Driscoll et al. 1984, Hess 1981, Hess and Alexander 1986, UNESCO 1973, Weste

Burns and Honkala 1990a, CONHP unpubl. data 2003, Carsey et al. 2003a, Hansen et al. 1988b, Johnston 1987, Kittel et al. 1997a, Kittel et al. 1999a, Mann

Bourgeron and Engelking 1994, Driscoll et al. 1984, Padgett et al. 1988b, Padgett et al. 1989, Western Ecology Working Group n.d.

Baker 1986, Baker 1989a, Baker 1989b, Bourgeron and Engelking 1994, Driscoll et al. 1984, Kittel and Lederer 1993, UNESCO 1973, Western Ecology Wor

Bigley and Hull 1995, Boss 1983, Christy 1979, Christy 2001a, Christy 2004, Christy et al. 1998, Cordes 1972, Driscoll et al. 1984, Frenkel et al. 1978, Kagan 

Bourgeron and Engelking 1994, Christy 2004, Christy and Putera 1993, Driscoll et al. 1984, Eilers 1975, Eilers 1984, Frenkel et al. 1978, Frenkel et al. 1984, 

Boggs 1996, Boggs 2000, Bourgeron and Engelking 1994, Shephard 1995, Western Ecology Working Group n.d., Worley 1977

Arno and Weaver 1990, Bourgeron and Engelking 1994, Bowerman et al. 1997, Burns and Honkala 1990a, Cooper 1975, Driscoll et al. 1984, Eyre 1980, Ha

Hopkins 1979a, Kagan et al. 2000, Western Ecology Working Group n.d.
Bourgeron and Engelking 1994, Driscoll et al. 1984, Lillybridge et al. 1995, Western Ecology Working Group n.d., Williams and Lillybridge 1983, Williams and 

Bourgeron and Engelking 1994, Brunstein and Yamaguchi 1992, CONHP unpubl. data 2003, Driscoll et al. 1984, Hess 1981, Hess and Alexander 1986, UNE

Bourgeron and Engelking 1994, Driscoll et al. 1984, Hopkins 1979a, Kagan and Borgais unpubl. data 1994, Kagan et al. 2000, Sawyer and Keeler-Wolf 1995

Western Ecology Working Group n.d.

Bourgeron and Engelking 1994, Christy 1979, Christy 2001a, Christy 2004, Christy et al. 1998, Driscoll et al. 1984, Egler 1934, Kagan et al. 2000, Sawyer an

Bassett et al. 1987, Bourgeron and Engelking 1994, Bourgeron et al. 1993b, Bourgeron et al. 1995, Driscoll et al. 1984, Stuever and Hayden 1997a, Western 

Bassett et al. 1987, Bourgeron and Engelking 1994, Bourgeron et al. 1993b, Bourgeron et al. 1995, Driscoll et al. 1984, Moir 1979, NMNHP unpubl. data, Nie

Bassett et al. 1987, Bourgeron and Engelking 1994, Bourgeron et al. 1993b, Bourgeron et al. 1995, Driscoll et al. 1984, Moir 1979, Moir and Carleton 1987, N

Bourgeron and Engelking 1994, CONHP unpubl. data, CONHP unpubl. data 2003, Driscoll et al. 1984, Isaacson 1967, Western Ecology Working Group n.d.

Bourgeron and Engelking 1994, Driscoll et al. 1984, Larson and Moir 1987, Western Ecology Working Group n.d.

Bourgeron and Engelking 1994, Driscoll et al. 1984, Kennedy 1983a, Kennedy 1983b, UNESCO 1973, Western Ecology Working Group n.d.

Bassett et al. 1987, Bourgeron and Engelking 1994, Bourgeron et al. 1995, Driscoll et al. 1984, Muldavin et al. 1992, Stuever and Hayden 1997b, Western Ec

Atzet et al. 1996, Jimerson et al. 1995, Kagan et al. 2004, Western Ecology Working Group n.d.

Western Ecology Working Group n.d.

Bourgeron and Engelking 1994, Driscoll et al. 1984, Hopkins 1979a, Kagan et al. 2000, Kovalchik 1987, Western Ecology Working Group n.d.

Atzet and Wheeler 1984, Bourgeron and Engelking 1994, Driscoll et al. 1984, Kagan et al. 2000, Mitchell and Moir 1976, Topik et al. 1988, Western Ecology 

Bourgeron and Engelking 1994, Driscoll et al. 1984, Lillybridge et al. 1995, Western Ecology Working Group n.d., Williams and Smith 1990

Bourgeron and Engelking 1994, Driscoll et al. 1984, Kagan et al. 2000, Topik et al. 1988, Western Ecology Working Group n.d.

Bourgeron and Engelking 1994, Driscoll et al. 1984, John and Tart 1986, Western Ecology Working Group n.d.

Atzet and McCrimmon 1990, Driscoll et al. 1984, John and Tart 1986, Kagan et al. 2000, Western Ecology Working Group n.d.

Bourgeron and Engelking 1994, Cooper and Pfister 1985, Driscoll et al. 1984, Hansen and Hoffman 1988, Hansen et al. 1984, Hoffman and Alexander 1987, 

CONHP unpubl. data 2003, Kittel et al. 1994, Kittel et al. 1997a, Kittel et al. 1999a, Western Ecology Working Group n.d.

Bourgeron and Engelking 1994, Driscoll et al. 1984, Fischer and Clayton 1983, Hansen and Hoffman 1988, Hansen et al. 1984, MTNHP 2002b, Pfister et al. 

Atzet and Wheeler 1984, Bourgeron and Engelking 1994, Driscoll et al. 1984, Franklin et al. 1972, Kagan et al. 2000, Waring 1969, Western Ecology Workin

Bourgeron and Engelking 1994, DeVelice et al. 1986, Driscoll et al. 1984, Johnson and Clausnitzer 1992, Kagan et al. 2000, Kartesz 1999, Larson and Moir 1

Bourgeron and Engelking 1994, Driscoll et al. 1984, Hopkins 1979a, Johnson and Clausnitzer 1992, Kagan et al. 2000, Western Ecology Working Group n.d

Bourgeron and Engelking 1994, Daubenmire and Daubenmire 1968, Driscoll et al. 1984, Franklin and Dyrness 1973, Hall 1973, Johnson and Clausnitzer 199

Bourgeron and Engelking 1994, Driscoll et al. 1984, Hall 1973, Head 1959, Kagan et al. 2000, Western Ecology Working Group n.d.

Bassett et al. 1987, Bourgeron and Engelking 1994, DeVelice et al. 1986, Driscoll et al. 1984, Muldavin et al. 1992, Muldavin et al. 1996, Western Ecology W

Bourgeron and Engelking 1994, Cooper and Pfister 1985, Cooper et al. 1987, Crane and Fischer 1986, Daubenmire 1952, Daubenmire and Daubenmire 196

Bourgeron and Engelking 1994, Driscoll et al. 1984, Dyrness 1960, Dyrness and Youngberg 1966, Hopkins 1979b, Kagan et al. 2000, Volland 1976, Volland 

Bourgeron and Engelking 1994, Driscoll et al. 1984, Kagan et al. 2000, Volland 1976, Volland 1985, Western Ecology Working Group n.d.

Bourgeron and Engelking 1994, Dealy 1971, Driscoll et al. 1984, Hall 1973, Johnson and Clausnitzer 1992, Kagan et al. 2000, Western Ecology Working Gro

Bourgeron and Engelking 1994, Driscoll et al. 1984, Hopkins 1979a, Kagan et al. 2000, Western Ecology Working Group n.d.

Muldavin et al. 2000a, NMNHP unpubl. data, Western Ecology Working Group n.d.

Bourgeron and Engelking 1994, Bourgeron et al. 1993b, Bourgeron et al. 1995, Brown et al. 1979, Dick-Peddie 1993, Driscoll et al. 1984, NMNHP unpubl. da

Durkin et al. 1995b, Muldavin et al. 1998a, NMNHP unpubl. data, Western Ecology Working Group n.d.

Bourgeron and Engelking 1994, CONHP unpubl. data 2003, Carsey et al. 2003a, Cooper and Cottrell 1990, Durkin et al. 1994b, Durkin et al. 1995a, Girard e

Bourgeron and Engelking 1994, Driscoll et al. 1984, IDCDC 2005, Padgett et al. 1989, Western Ecology Working Group n.d.

Bourgeron and Engelking 1994, CONHP unpubl. data 2003, Carsey et al. 2003a, Carsey et al. 2003b, Driscoll et al. 1984, Girard et al. 1997, Jones 1992b, K

Bourgeron and Engelking 1994, Driscoll et al. 1984, Jones 1992b, Jones and Ogle 2000, Manning and Padgett 1992, Manning and Padgett 1995, Nachlinger 

CONHP unpubl. data 2003, Carsey et al. 2003a, Kittel et al. 1999a, Kittel et al. 1999b, Western Ecology Working Group n.d.

Bourgeron and Engelking 1994, Crawford 2001, Crawford 2003, Crowe and Clausnitzer 1997, Crowe et al. 2002, Crowe et al. 2004, Driscoll et al. 1984, Evan

Bourgeron and Engelking 1994, Cooper and Pfister 1981, Driscoll et al. 1984, Lynch 1955, MTNHP 2002b, UNESCO 1973, Western Ecology Working Group 

Green and Klinka 1994, Kagan et al. 2000, Titus and Christy 1997, Titus et al. 1996, WNHP unpubl. data, Western Ecology Working Group n.d.

Bourgeron and Engelking 1994, Driscoll et al. 1984, Franklin and Dyrness 1973, Western Ecology Working Group n.d.

Chappell 1999, Fonda 1974, Western Ecology Working Group n.d.

Kovalchik 2001, Kovalchik pers. comm., MacKenzie pers. comm., Western Ecology Working Group n.d.

Campbell and Dick-Peddie 1964, Dick-Peddie 1993, Laurenzi et al. 1983, Muldavin et al. 2000a, NMNHP unpubl. data, Szaro 1989, Western Ecology Workin

Dick-Peddie 1993, Muldavin et al. 2000a, Western Ecology Working Group n.d.

Bourgeron and Engelking 1994, CONHP unpubl. data 2003, Carsey et al. 2003a, Christy 1973, Crouch 1961a, Crouch 1961b, Crouch 1978, Crouch 1979a, C

CONHP unpubl. data 2003, Carsey et al. 2003a, Muldavin et al. 2000a, NMNHP unpubl. data, Western Ecology Working Group n.d.
Muldavin et al. 2000a, NMNHP unpubl. data, Western Ecology Working Group n.d.

CONHP unpubl. data 2003, Carsey et al. 2003a, Kittel et al. 1996, Kittel et al. 1999a, Western Ecology Working Group n.d.

Bourgeron and Engelking 1994, Driscoll et al. 1984, Godfrey et al. 2000, Hansen et al. 1991, Hansen et al. 1995, Kudray et al. 2004, MTNHP 2002b, MTNHP 

Muldavin et al. 2000a, Western Ecology Working Group n.d.

Donnelly et al. 2006, Muldavin et al. 2000a, NMNHP unpubl. data, Western Ecology Working Group n.d.

Muldavin et al. 2000a, NMNHP unpubl. data, Western Ecology Working Group n.d.

Bourgeron and Engelking 1994, CONHP unpubl. data 2003, Carsey et al. 2003a, Driscoll et al. 1984, Keammerer 1974a, Keammerer 1974b, Kittel and Lede

Muldavin et al. 2000a, NMNHP unpubl. data, Western Ecology Working Group n.d.

Muldavin et al. 2000a, Western Ecology Working Group n.d.

Boles and Dick-Peddie 1983, Bourgeron and Engelking 1994, Cogan et al. 2004, Driscoll et al. 1984, Muldavin et al. 2000a, Szaro 1989, Western Ecology W

Bourgeron and Engelking 1994, Brown et al. 1979, Dick-Peddie 1993, Driscoll et al. 1984, Henry 1981, Muldavin 1987, Muldavin et al. 2000a, NMNHP unpub

Brown et al. 1979, Campbell and Dick-Peddie 1964, Dick-Peddie 1993, Laurenzi et al. 1983, Muldavin et al. 2000a, NMNHP unpubl. data, Reichenbacher 19

Campbell and Dick-Peddie 1964, Dick-Peddie 1993, Muldavin et al. 2000a, NMNHP unpubl. data, Reichenbacher 1984, Szaro 1989, Western Ecology Worki

Allard 1990, Boles and Dick-Peddie 1983, Bourgeron and Engelking 1994, CONHP unpubl. data 2003, Campbell and Dick-Peddie 1964, Diamond 1993, Diam

Bourgeron and Engelking 1994, Driscoll et al. 1984, Henry 1981, Western Ecology Working Group n.d.

Bourgeron and Engelking 1994, Campbell and Dick-Peddie 1964, Dick-Peddie 1993, Driscoll et al. 1984, Evens and San 2006, Klein and Evens 2006, Mulda

Bourgeron and Engelking 1994, Bourgeron et al. 1993b, Bourgeron et al. 1995, Driscoll et al. 1984, NMNHP unpubl. data, Reid et al. 1994, Sawyer and Keele

Bourgeron and Engelking 1994, Driscoll et al. 1984, Mueggler 1988, Steele et al. 1983, Western Ecology Working Group n.d., Youngblood and Mueggler 198

Bourgeron and Engelking 1994, Driscoll et al. 1984, Eddleman and Jaindl 1994, Mueggler 1988, Peterson pers. comm., Western Ecology Working Group n.d

Bourgeron and Engelking 1994, Driscoll et al. 1984, Mueggler 1988, Mueggler and Campbell 1986, Western Ecology Working Group n.d.

Christy 2001a, Christy 2004, Kagan et al. 2004, Western Ecology Working Group n.d.

Bailey et al. 1994, Bourgeron and Engelking 1994, Crowe and Clausnitzer 1997, Crowe et al. 2004, Driscoll et al. 1984, Kagan et al. 2000, Kovalchik 1987, K

Bourgeron and Engelking 1994, Bunin 1975a, Bunin 1975c, CONHP unpubl. data, CONHP unpubl. data 2003, Driscoll et al. 1984, Johnston 1987, Western E

Bourgeron and Engelking 1994, Driscoll et al. 1984, Western Ecology Working Group n.d., Youngblood and Mueggler 1981

Bourgeron and Engelking 1994, CONHP unpubl. data 2003, Driscoll et al. 1984, Powell 1988a, Reid et al. 1994, Sarr and Sanderson 1998, UNESCO 1973, W

Bourgeron and Engelking 1994, Driscoll et al. 1984, Mueggler 1988, Western Ecology Working Group n.d.

Bourgeron and Engelking 1994, Driscoll et al. 1984, Mueggler 1988, Mueggler and Campbell 1986, Western Ecology Working Group n.d.

Western Ecology Working Group n.d.

Bourgeron and Engelking 1994, Chappell 2006b, Chappell and Crawford 1997, Driscoll et al. 1984, Kagan et al. 2000, ORNHP unpubl. data, Reigel et al. 199

Bourgeron and Engelking 1994, Driscoll et al. 1984, Frenkel 1976, Kagan et al. 2000, Mahony and Stuart 2000, Western Ecology Working Group n.d.

Atzet and Wheeler 1984, Bourgeron and Engelking 1994, Driscoll et al. 1984, Kagan et al. 2000, Western Ecology Working Group n.d.

Bourgeron and Engelking 1994, Chappell 1997, Chappell 2006b, Driscoll et al. 1984, Franklin and Dyrness 1973, Hemstrom et al. 1987, Henderson et al. 198

Bourgeron and Engelking 1994, Chappell 1994, Driscoll et al. 1984, WNHP unpubl. data, Western Ecology Working Group n.d.

Atzet et al. 1996, Christy et al. 1998, Hemstrom and Logan 1986, Western Ecology Working Group n.d., Wiedemann 1984, Wiedemann 1990, Wiedemann 1

Bourgeron and Engelking 1994, Chappell 1994, Chappell 1997, Chappell 2001, Chappell 2006b, Driscoll et al. 1984, WNHP unpubl. data, Western Ecology W

Bourgeron and Engelking 1994, Driscoll et al. 1984, Fischer and Clayton 1983, MTNHP 2002b, Pfister et al. 1977, Roberts 1980, Soil Conservation Service 1

Bourgeron and Engelking 1994, Driscoll et al. 1984, Kagan et al. 2000, Topik 1989, Topik et al. 1988, Western Ecology Working Group n.d.

Bourgeron and Engelking 1994, Chappell 1997, Chappell 2001, Chappell 2006b, Driscoll et al. 1984, Fonda and Bernardi 1976, Franklin and Dyrness 1973, H

Bourgeron and Engelking 1994, Driscoll et al. 1984, Lesica and DeVelice 1992, MTNHP 2002b, Western Ecology Working Group n.d.

Bourgeron and Engelking 1994, Bunin 1975c, CONHP unpubl. data 2003, Daubenmire 1952, Driscoll et al. 1984, Hess and Wasser 1982, Hoffman and Alex

Driscoll et al. 1984, Hansen and Hoffman 1988, Hansen et al. 1984, MTNHP 2002b, Montagne et al. 1982, Roberts 1980, Roberts et al. 1979a, UNESCO 19

Bassett et al. 1987, Bourgeron and Engelking 1994, Bourgeron et al. 1993b, Bourgeron et al. 1995, Driscoll et al. 1984, Muldavin et al. 1996, NMNHP unpubl

Bourgeron and Engelking 1994, Chappell 1994, Driscoll et al. 1984, Henderson et al. 1989, WNHP unpubl. data, Western Ecology Working Group n.d.

Bourgeron and Engelking 1994, Crowe and Clausnitzer 1997, Crowe et al. 2004, Driscoll et al. 1984, Ganskopp 1979, Hemstrom et al. 1987, Kagan et al. 20

Bourgeron and Engelking 1994, Bourgeron et al. 1993b, Bourgeron et al. 1995, Driscoll et al. 1984, Western Ecology Working Group n.d.

Chappell 2006b, Chappell and Crawford 1997, Chappell et al. n.d., Kagan et al. 2000, WNHP unpubl. data, Western Ecology Working Group n.d.

Bourgeron and Engelking 1994, Driscoll et al. 1984, Jimerson 1993, Kagan et al. 2000, Reigel et al. 1992, Smith 1985, Western Ecology Working Group n.d.

Barbour and Major 1988, Bourgeron and Engelking 1994, Detling 1961, Driscoll et al. 1984, Kagan et al. 2000, ORNHP unpubl. data, Riegel et al. 1991, Wes

Chappell 2006b, Chappell and Crawford 1997, Chappell et al. n.d., Roemer 1972, WNHP unpubl. data, Western Ecology Working Group n.d.

Kagan et al. 2000, Western Ecology Working Group n.d.

Bourgeron and Engelking 1994, Driscoll et al. 1984, John and Tart 1986, Lillybridge et al. 1995, WNHP unpubl. data, Western Ecology Working Group n.d.

Bourgeron and Engelking 1994, Driscoll et al. 1984, Kagan et al. 2000, ORNHP unpubl. data, Riegel et al. 1991, Thilenius 1968, WNHP unpubl. data, Weste
Cheatham and Haller 1975, Conard et al. 1980, Davis et al. 1998, Griffin 1988, Griffin and Critchfield 1972, Griffins 1976, Holland 1986b, Reid et al. 1994, Sa

Cheatham and Haller 1975, Griffin and Critchfield 1972, Minnich 1980, Philbrick and Haller 1988, Sawyer and Keeler-Wolf 1995, Western Ecology Working G

Christy 2004, Christy and Putera 1993, Kagan et al. 2000, Kunze 1994, Western Ecology Working Group n.d.

Western Ecology Working Group n.d.

Atzet and McCrimmon 1990, Bourgeron and Engelking 1994, Driscoll et al. 1984, Kagan et al. 2000, Western Ecology Working Group n.d.

Atzet and McCrimmon 1990, Bourgeron and Engelking 1994, Driscoll et al. 1984, Kagan et al. 2000, Western Ecology Working Group n.d.

Bourgeron and Engelking 1994, Cooper et al. 1987, Driscoll et al. 1984, IDCDC 2005, Steele 1971, Western Ecology Working Group n.d.

Bourgeron and Engelking 1994, Cooper et al. 1987, Driscoll et al. 1984, Hansen et al. 1995, Kovalchik 1993, MTNHP 2002b, Pfister et al. 1977, WNHP unpu

Atzet and McCrimmon 1990, Bourgeron and Engelking 1994, Driscoll et al. 1984, Kagan et al. 2000, Western Ecology Working Group n.d., Williams 1978, W

Bourgeron and Engelking 1994, Cooper et al. 1987, Crawford and Johnson 1985, Driscoll et al. 1984, Western Ecology Working Group n.d.

Bourgeron and Engelking 1994, Cooper et al. 1987, Driscoll et al. 1984, Western Ecology Working Group n.d., Williams and Lillybridge 1985, Williams and S

Atzet and Wheeler 1984, Atzet et al. 1996, Bourgeron and Engelking 1994, Driscoll et al. 1984, Kagan et al. 2000, Western Ecology Working Group n.d.

Bourgeron and Engelking 1994, Driscoll et al. 1984, Kovalchik 1993, Lillybridge et al. 1995, Western Ecology Working Group n.d., Williams and Lillybridge 19

Bourgeron and Engelking 1994, Cooper et al. 1987, Driscoll et al. 1984, Franklin and Dyrness 1973, Henderson et al. 1986, Henderson et al. 1989, WNHP u

Bourgeron and Engelking 1994, Cooper et al. 1987, Driscoll et al. 1984, IDCDC 2005, Western Ecology Working Group n.d.
 Hebda 1999, COSEWIC 2002, Cadrin and Wolowicz 2005, Green and Klinka 1994, Meidinger et al. 2005, Western Ecology Working Group n.d.

al. 1993, Cadrin and Wolowicz 2005, Dorner and Wong 2003, Green and Klinka 1994, Lertzman et al. 2002, Meidinger et al. 2005, Western Ecology Working Group n.d.

AP 2002, Green and Klinka 1994, Meidinger et al. 2005, Roemer 1972, Western Ecology Working Group n.d.

EWIC 2002, Cadrin and Wolowicz 2005, Green and Klinka 1994, Meidinger et al. 2005, Ward et al. 1998, Western Ecology Working Group n.d.

n and Wolowicz 2005, Chappell 1997, Chappell 2005, Green and Klinka 1994, Meidinger et al. 2005, Ward et al. 1998, Western Ecology Working Group n.d.

 Wolowicz 2005, Dorner and Wong 2003, Green and Klinka 1994, Lertzman et al. 2002, Meidinger et al. 2005, Western Ecology Working Group n.d.

entch et al. 2002, Stephenson and Adams 1986, TNC 1994

p n.d., Edinger et al. 2002, Greller 1977, NRCS 2001b, Reschke 1990, Sirkin 1972, Sneddon and Lundgren 2001, Stalter 1979

., Fleming et al. 2001, Harrison 2004, Harrison and Stango 2003, Higgins et al. 1971, Hill 1986, Klotz 1986, Schafale and Weakley 1990, TNC 1995c

985, Eastern Ecology Working Group n.d., Fleming et al. 2001, Harrison 2004, Higgins et al. 1971, Hill 1986, Klotz 1986, Rawinski 1992, Sneddon et al. 1994, Stalter 1979

pers. comm., VDNH 2003, Ware and Ware 1992

, Thilenius 1972

ier 2000, WYNDD unpubl. data

, Heikens and Robertson 1994, Heikens et al. 1994, Homoya 1994, Homoya et al. 1985, Hutchison 1994, Hutchison et al. 1986, Illinois Nature Preserve Commission 1973, K

urner et al. 1997, Turner et al. 1999, Turner et al. unpubl. data

yre 1980, McLeod 1988, NCNHP 1993, Nicholas et al. 1992, Oosting and Billings 1951, Pyne 1994, Ramseur 1960, Schafale 1998b, Schafale and Weakley 1990, Southeaste

n 1941, Bruck 1988, Busing et al. 1988, Crandall 1958, Davis 1930, Dull et al. 1988a, Eyre 1980, Fleming and Coulling 2001, Fleming et al. 2001, McLeod 1988, NCNHP 199

le and Weakley 1990, Southeastern Ecology Working Group n.d., TDNH unpubl. data

d Muller 1993a, Robertson 1953, Snyder et al. 1990, Southeastern Ecology Working Group n.d.

rs. comm., Southeastern Ecology Working Group n.d.

.d., Wentworth et al. 1993

outheastern Ecology Working Group n.d.
 Golden 1981, McLeod 1988, Peet et al. unpubl. data 2002, Pittillo and Smathers 1979, Pyne 1994, Ramseur 1960, Rawinski 1992, Rheinhardt 1981, Russell 1953, Schafale 

 Lindsay and Bratton 1979a, McLeod 1988, Peet et al. unpubl. data 2002, Pittillo and Smathers 1979, Pyne 1994, Ramseur 1960, Rawinski 1992, Rheinhardt 1981, Russell 1

 Olmsted and Loope 1984, Southeastern Ecology Working Group n.d.

l. data, Wharton 1978

andall 1960, Davis 1930, Dull et al. 1988b, Eagar and Adams 1992, Eyre 1980, Korstian 1937, McLeod 1988, NCNHP 1993, NatureServe Ecology - Southeastern U.S. unpub

l. unpubl. data 2002, Southeastern Ecology Working Group n.d., TDNH unpubl. data

n.d., TDNH unpubl. data

ers. comm., Schotz pers. comm., Southeastern Ecology Working Group n.d., TDNH unpubl. data

 Turner et al. 1999, Turner et al. unpubl. data

Sparks et al. 1998, Zollner pers. comm.

pe et al. 1979, Snyder et al. 1990, Southeastern Ecology Working Group n.d., TNC n.d.

9, Snyder et al. 1990, Southeastern Ecology Working Group n.d., TNC n.d.

1990, Reed 1982, Soil Conservation Service 1990, Southeastern Ecology Working Group n.d., Turner 1935a, Turner et al. unpubl. data, USFS 1988

Schafale 1994, Schafale 2000, Southeastern Ecology Working Group n.d.

 Ecology Working Group n.d.

publ. data 2002, Southeastern Ecology Working Group n.d.

2000, Schafale and Weakley 1990, Southeastern Ecology Working Group n.d.

publ. data 2002, Southeastern Ecology Working Group n.d.

eet 1996, Peet et al. unpubl. data 2002, Ravenel 1850, Southeastern Ecology Working Group n.d.

 1981a, Southeastern Ecology Working Group n.d.
90, Southeastern Ecology Working Group n.d.

d Peterson 1998

m., Southeastern Ecology Working Group n.d.

94, Schafale 2000, Southeastern Ecology Working Group n.d., Weakley 1997

e 1998b, Schafale 2002, Schafale and Weakley 1990, Southeastern Ecology Working Group n.d., TDNH unpubl. data, USFS 1988

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 Wiedemann 1990, Wiedemann 1993

P unpubl. data, Western Ecology Working Group n.d.

1980, Soil Conservation Service 1981b, Western Ecology Working Group n.d.

rking Group n.d.

976, Franklin and Dyrness 1973, Henderson et al. 1986, Krajina 1969, WNHP unpubl. data, Western Ecology Working Group n.d.

 Wasser 1982, Hoffman and Alexander 1980, Komarkova et al. 1988a, Tisdale and McLean 1957, Western Ecology Working Group n.d.

Roberts et al. 1979a, UNESCO 1973, Western Ecology Working Group n.d.

davin et al. 1996, NMNHP unpubl. data, Reid et al. 1994, Stuever and Hayden 1997b, UNESCO 1973, Western Ecology Working Group n.d.

Ecology Working Group n.d.

strom et al. 1987, Kagan et al. 2000, Kovalchik 2001, Titus et al. 1998, Topik et al. 1988, Western Ecology Working Group n.d.

gy Working Group n.d.

stern Ecology Working Group n.d.

ubl. data, Riegel et al. 1991, Western Ecology Working Group n.d.

orking Group n.d.

ern Ecology Working Group n.d.

968, WNHP unpubl. data, Western Ecology Working Group n.d.
olland 1986b, Reid et al. 1994, Sawyer and Keeler-Wolf 1995, Warner and Hendrix 1984, Western Ecology Working Group n.d.

995, Western Ecology Working Group n.d.

b, Pfister et al. 1977, WNHP unpubl. data, Western Ecology Working Group n.d., Williams and Lillybridge 1985, Williams et al. 1990b, Williams et al. 1995

king Group n.d., Williams 1978, Williams and Winward 1976

rking Group n.d.

d Lillybridge 1985, Williams and Smith 1990, Williams et al. 1990b

 Ecology Working Group n.d.

p n.d., Williams and Lillybridge 1985, Williams and Smith 1990

 Henderson et al. 1989, WNHP unpubl. data, Western Ecology Working Group n.d., Williams and Lillybridge 1985, Williams et al. 1990b
rking Group n.d.

5, Western Ecology Working Group n.d.

Ecology Working Group n.d.

 Working Group n.d.

ey 1990, TNC 1995c

ki 1992, Sneddon et al. 1994, Stalter 1979

Illinois Nature Preserve Commission 1973, Kuchler 1964, Madany 1981, Midwestern Ecology Working Group n.d., Mohlenbrock 1986, Nelson 1985, Robertson and Heikens 

98b, Schafale and Weakley 1990, Southeastern Ecology Working Group n.d., TDNH unpubl. data, USFS 1988, Weakley 1993, White 1984a, White 1984b, White and Pickett 

eming et al. 2001, McLeod 1988, NCNHP 1993, Nicholas et al. 1992, Oosting and Billings 1951, Peet et al. unpubl. data 2002, Pyne 1994, Ramseur 1960, Rawinski 1992, Rh
92, Rheinhardt 1981, Russell 1953, Schafale 1998b, Schafale and Weakley 1990, Schafale pers. comm., Schofield 1960, Singer et al. 1984, Southeastern Ecology Working 

0, Rawinski 1992, Rheinhardt 1981, Russell 1953, Schafale 1998b, Schafale and Weakley 1990, Schafale pers. comm., Schofield 1960, Singer et al. 1984, Southeastern Eco

ureServe Ecology - Southeastern U.S. unpubl. data, Nicholas and Zedaker 1989, Nicholas et al. 1992, Oosting and Billings 1951, Peet et al. unpubl. data 2002, Pyne 1994, R

bl. data, USFS 1988
962, Rice and Penfound 1959, Southeastern Ecology Working Group n.d.
987, UNESCO 1973, Western Ecology Working Group n.d.

997, Miller 1976, Moseley 1998, Neiman 1987, Titus et al. 1998, UNESCO 1973, Western Ecology Working Group n.d.

g Group n.d., Willing 1987
y Working Group n.d.

rtzman et al. 2002, Meidinger et al. 2005, Pojar and Banner 1984, Western Ecology Working Group n.d.

 Working Group n.d.

eidinger et al. 2005, Western Ecology Working Group n.d.
5, Western Ecology Working Group n.d.

5, Pojar and Banner 1984, Western Ecology Working Group n.d.

, Sperduto and Nichols 2004, Sperduto and Ritter 1994

007, Rawinski 1984, Roberts 1914, Swain and Kearsley 2001, Thompson 1996, Thompson and Sorenson 2000, Walz 1996

1994, Richardson and Gibbons 1993, Robinette 1966, Schafale 1998a, Schafale and Weakley 1990, Stotler and Crandall-Stotler 1977, TDNH unpubl. data, USFS 1988, Wal

985b, MENHP 1991, Martin 1959b, McDonnell 1979, Motzkin and Foster 2002, Nelson and Fink 1980, RINHP n.d., Rawinski 1984, Reschke 1990, Swain and Kearsley 2001

 1971, Hill 1986, J. Harrison pers. comm., Klotz 1986, Schafale and Weakley 1990, Stalter 1990, Stalter and Lamont 1990

RCS 2001b, Rawinski 1984, Reschke 1990, Sperduto 1997b, Stalter 1979, Svenson 1970, Swain and Kearsley 2001

TNHP 2002b, MTNHP unpubl. data, Mack 1981, Midwestern Ecology Working Group n.d., NDNHI n.d., Nixon 1967a, Steinauer 1989, Steinauer and Rolfsmeier 2000, Tolstea

 Group n.d., NDNHI n.d., Thilenius 1970, Thilenius and Brown 1990, Thilenius and Smith 1985, Thilenius et al. 1995
 al. 1981, Midwestern Ecology Working Group n.d., Miller and Tehon 1929, Minckler 1957, Mohlenbrock 1986, Mohlenbrock and Voigt 1959, Nelson 1985, Niering 1979, Plat

ennedy 1973, Klahr 1989, Kuchler 1964, Luckhardt and Barclay 1937, Midwestern Ecology Working Group n.d., Nelson 1985, Penfound 1962, Rice and Penfound 1959, Rob

rking Group n.d., Nelson 1985, Taft et al. 1995, White and Madany 1978

a, VDNH 2003, Walker 1987

stern U.S. unpubl. data, Peet et al. unpubl. data 2002, Pittillo and Smathers 1979, Pyne 1994, Rawinski 1992, Rheinhardt and Ware 1984, Schafale 1998b, Schafale and We

and Weakley 1990, Southeastern Ecology Working Group n.d., USFS 1988, Wharton 1978, Wharton et al. 1982, Whitehead 1972, ter Braak and Gremmen 1987

94b, Wieland 2000b, Wiseman 1986

m., Southeastern Ecology Working Group n.d., TDNH unpubl. data, Tucker pers. comm., Wieland 1994a, Wieland 1994b, Zollner pers. comm.

mith 1996a, Southeastern Ecology Working Group n.d., Turner et al. 1999, USFS 1988
0, Fleming and Coulling 2001, Fleming et al. 2001, Golden 1974, Korstian 1937, McLaughlin et al. 1987, McLeod 1988, NCNHP 1993, NatureServe Ecology - Southeastern U

., TDNH unpubl. data

e 1998b, Schafale and Weakley 1990, Southeastern Ecology Working Group n.d., Stephenson and Adams 1984, Stephenson and Clovis 1983, TDNH unpubl. data, White a

son and Clovis 1983, Stevens 1969

omm., Soil Conservation Service 1990, Southeastern Ecology Working Group n.d., Turner 1935a, Turner et al. 1999, Turner et al. unpubl. data, USFS 1988

oup n.d., TDNH unpubl. data, Taylor 1965, Turner et al. 1997, Zanoni et al. 1979
er et al. 1999, USFS 1988

theastern Ecology Working Group n.d., Varner et al. 2003a, Varner et al. 2003b, Wharton 1978

eastern Ecology Working Group n.d., Stewart pers. comm., Turner et al. 1999

1986b, Soil Conservation Service 1990, Southeastern Ecology Working Group n.d., Turner et al. 1999, USFS 1988
orking Group n.d., Turner et al. 1999, USFS 1988

orking Group n.d., Turner et al. 1999, USFS 1988

NH unpubl. data

ner et al. 1999, Turner et al. unpubl. data, USFS 1988

gy Working Group n.d., TDNH unpubl. data
ubl. data 2002, Pyne 1994, Rohrer 1983, Schafale 1998b, Schafale and Weakley 1990, Southeastern Ecology Working Group n.d., TDNH unpubl. data, USFS 1988, Weakle

bl. data 2002, Rayner 1984, Rayner and Batson 1976, Sandifer et al. 1980, Schafale and Weakley 1990, Schotz pers. comm., Sharitz 1975, Soil Conservation Service 1980

 Wells and Shunk 1938, Wentworth et al. 1993
npubl. data, USFS 1988, VDNH 2003, Weakley and Schafale 1994
ern Ecology Working Group n.d.

estern Ecology Working Group n.d.

05, Johnson and Clausnitzer 1992, Johnson and Simon 1985, Johnson and Simon 1987, Kagan et al. 2000, MTNHP 2002b, McCune and Allen 1985, Titus et al. 1998, UNES

1990, Richard et al. 1996, Richter 1999, UNESCO 1973, Western Ecology Working Group n.d.

Ecology Working Group n.d.

981, Steele et al. 1983, Titus et al. 1998, Western Ecology Working Group n.d.

Ecology Working Group n.d.

cology Working Group n.d., Wiedemann 1984

7, Rust 1998, Schlatterer 1972, Schmidt and McDonald 1990, Steele et al. 1981, Steele et al. 1983, Western Ecology Working Group n.d.
84, Wiedemann 1993

Working Group n.d., Willing 1987

ology Working Group n.d.

NESCO 1973, WNHP unpubl. data, Western Ecology Working Group n.d., Williams et al. 1990b

teele et al. 1981, WNHP unpubl. data, Western Ecology Working Group n.d., Williams and Lillybridge 1985

991, Muldavin et al. 2000a, Western Ecology Working Group n.d.

00a, Walford 1996, Western Ecology Working Group n.d.

ern Ecology Working Group n.d.

 IDCDC 2005, IDCDC unpubl. data 2002, Jankovsky-Jones et al. 2001, Kagan et al. 2000, Kauffman 1982, Kauffman et al. 1985, Kovalchik 1987, Kovalchik 2001, Moseley 1

, Jones and Walford 1995, Lindauer 1970, Lindauer 1983, Lindauer and Christy 1972, Lindauer and Fitzgerald 1974, Lindauer and Ward 1968, Lindauer et al. 1973, Masek 1
estern Ecology Working Group n.d.

Szaro 1989, TNC 1992b, Western Ecology Working Group n.d.

bb and Brotherson 1988, Western Ecology Working Group n.d.

2, WNHP unpubl. data, Western Ecology Working Group n.d.

rn Ecology Working Group n.d.
990b, Williams et al. 1995
 1986, Nelson 1985, Robertson and Heikens 1994, Schwegman 1973, TNC 1985, TNC 1995a, UNESCO 1973, Voigt and Mohlenbrock 1964, White and Madany 1978

White 1984a, White 1984b, White and Pickett 1985, White et al. 1993, Whittaker 1956

yne 1994, Ramseur 1960, Rawinski 1992, Rheinhardt and Ware 1984, Schafale 1998b, Schafale and Weakley 1990, Southeastern Ecology Working Group n.d., Stephenson 
r et al. 1984, Southeastern Ecology Working Group n.d., TDNH unpubl. data, USFS 1988, White et al. 1993, White pers. comm., Whittaker 1956

d 1960, Singer et al. 1984, Southeastern Ecology Working Group n.d., TDNH unpubl. data, USFS 1988, White et al. 1993, White pers. comm., Whittaker 1956

, Peet et al. unpubl. data 2002, Pyne 1994, Ramseur 1960, Rawinski 1992, Schafale 1998b, Schafale and Weakley 1990, Schofield 1960, Southeastern Ecology Working Gr



r 1977, TDNH unpubl. data, USFS 1988, Walton et al. 1997, Weakley and Schafale 1994

84, Reschke 1990, Swain and Kearsley 2001, Trudeau et al. 1977

989, Steinauer and Rolfsmeier 2000, Tolstead 1947, USACE 1979, Von Loh et al. 2000, Wali et al. 1980, Williams 1979
 Voigt 1959, Nelson 1985, Niering 1979, Platt and Brantley 1993, Robertson et al. 1984, SAF 1967, Schwartz and Schwartz 1959, TDNH unpubl. data, TNC 1995a, Thornbur

enfound 1962, Rice and Penfound 1959, Robertson and Heikens 1994, Smith pers. comm., TNC 1985, TNC 1995a, Turner pers. comm., UNESCO 1973, Voigt and Mohlenb

are 1984, Schafale 1998b, Schafale and Weakley 1990, Schafale pers. comm., Southeastern Ecology Working Group n.d., Stamper 1976, TDNH unpubl. data, VDNH 2003, 

72, ter Braak and Gremmen 1987
1993, NatureServe Ecology - Southeastern U.S. unpubl. data, Nicholas and Zedaker 1989, Nicholas et al. 1992, Oosting and Billings 1951, Peet et al. unpubl. data 2002, Pyn

nd Clovis 1983, TDNH unpubl. data, White and Pickett 1985, White et al. 1985, Whittaker 1956

. unpubl. data, USFS 1988


d., TDNH unpubl. data, USFS 1988, Weakley 1980, Weakley 1997, Whittaker 1956

Sharitz 1975, Soil Conservation Service 1980, Soil Conservation Service 1982, South Carolina Wildlife and Marine Resources Department 1984, Southeastern Ecology Work

Cune and Allen 1985, Titus et al. 1998, UNESCO 1973, Western Ecology Working Group n.d., Zamora 1975
, Kovalchik 1987, Kovalchik 2001, Moseley 1998, Moseley and Bursik 1994, Poulton 1955, Sunderman 2000, Titus et al. 1998, WNHP unpubl. data 2002, Walford et al. 2001

nd Ward 1968, Lindauer et al. 1973, Masek 1979, McEachern 1979, Reid et al. 1994, Steinauer pers. comm., UNESCO 1973, Western Ecology Working Group n.d.


nbrock 1964, White and Madany 1978

ern Ecology Working Group n.d., Stephenson and Adams 1984, TDNH unpubl. data, USFS 1988, VDNH 2003, Weakley 1993, White 1984a, White 1984b, White and Pickett 
, Whittaker 1956

e pers. comm., Whittaker 1956

field 1960, Southeastern Ecology Working Group n.d., Stephenson and Adams 1984, Stephenson and Clovis 1983, Stotler and Crandall-Stotler 1977, TDNH unpubl. data, US




9, TDNH unpubl. data, TNC 1995a, Thornbury 1965, Voigt and Mohlenbrock 1964, Wharton et al. 1982, White and Madany 1978, Yeager 1949

 comm., UNESCO 1973, Voigt and Mohlenbrock 1964, White and Madany 1978

mper 1976, TDNH unpubl. data, VDNH 2003, Wharton 1978, Wood 1975
ings 1951, Peet et al. unpubl. data 2002, Pyne 1994, Ramseur 1960, Rawinski 1992, Rheinhardt and Ware 1984, Schafale 1998b, Schafale and Weakley 1990, Schofield 19


epartment 1984, Southeastern Ecology Working Group n.d., Wharton 1978


WNHP unpubl. data 2002, Walford et al. 2001, Western Ecology Working Group n.d.

estern Ecology Working Group n.d.


White 1984a, White 1984b, White and Pickett 1985, White et al. 1993, Whittaker 1956
Crandall-Stotler 1977, TDNH unpubl. data, USFS 1988, Wentworth et al. 1988, White 1984a, White 1984b, White and Cogbill 1992, White and Pickett 1985, White et al. 1993





8b, Schafale and Weakley 1990, Schofield 1960, Southeastern Ecology Working Group n.d., Stephenson and Adams 1984, Stephenson and Clovis 1983, TDNH unpubl. data









92, White and Pickett 1985, White et al. 1993, Whittaker 1956, Zedaker et al. 1988





henson and Clovis 1983, TDNH unpubl. data, USFS 1988, VDNH 2003, Wentworth et al. 1988, White 1984a, White 1984b, White and Cogbill 1992, White and Pickett 1985, 















te and Cogbill 1992, White and Pickett 1985, White et al. 1993, Whittaker 1956, Zedaker et al. 1988
Resp = Classification 

Responsibility

NatureServe Explorer link

Global Scientific Name

Common Name

Confidence

Summary

Global Rank

Rounded Global Rank

Global Rank Review Date

Global Rank Reasons

Nations
Subnations

TNC Ecoregions 

USFS Ecoregions

Citations
In this context, a way to group the list of associations by region. Technically, the name of the region which has been 

assigned lead responsibility for the classification of the Association. Values: East (CT, DC, DE, MA, MD, ME, NH, NJ, 

NY, PA, RI, VT, WV), Midwest (IA, IL, IN, KS, MI, MN, MO, ND, NE, OH, SD, WI), Southeast (AR, FL, GA, KY, LA, 

MS, NC, OK, SC, TN, TX, VA), West (, AZ, CA, CO, HI, ID, MT, NM, NV, OR, UT, WA, WY), Canada

Will bring you directly to the report for this association on NatureServe Explorer, where more details about the 

association can be found.

The global name of the Association includes the scientific names of dominant and diagnostic species. Species 

occurring in the same stratum are separated by a hyphen ( - ), and those occurring in different strata are 

separated by a slash ( / ); hyphens and slashes are surrounded by spaces. Species occurring in the uppermost 

strata are listed first, followed successively by those in lower strata. Within the same stratum, the order of 

species names generally reflects decreasing levels of dominance, constancy, or indicator value. In physiognomic 

types where there is a dominant herbaceous layer with a scattered woody layer, Association names can be based 

on species found in either the herbaceous layer or the woody layer, whichever is more diagnostic of the type. If 

both layers are used, then the uppermost layer is always listed first, regardless of which may be more diagnostic.

Species less consistently found in all occurrences of the Association are placed in parentheses (). In cases where 

a particular genus is dominant or diagnostic, but individual species of the genus may vary among occurrences, 

only the specific epithets are placed in parentheses.

Vascular plant species nomenclature for Association and Alliance names follows the nationally standardized list 

of Kartesz (1999), with very few exceptions. Nomenclature for nonvascular plants follows Anderson (1990) and 

Anderson et al. (1990) for mosses, Egan (1987, 1989, 1990, 1991) and Esslinger and Egan (1995) for lichens, 

and Stotler and Crandall-Stotler (1977) for liverworts/hornworts.

A common or colloquial name for the Association. Not comprehensively filled out.

The degree of confidence associated with the classification of the Association. This confidence is based on the 

quality and type of data used in the analysis, as well as the extent to which the entire (or potential) range of the 

Association was considered.

1 = STRONG: Classification is based on quantitative analysis of verifiable, high-quality field data (species lists 

and associated environmental information) from plots that are published in full or are archived in a publicly 

accessible database. A sufficient number of high-quality plots covering the expected geographic distribution and 

habitat variability of the vegetation type, as well as plots from related types across the region, have been used in 

the analysis.

2 = MODERATE: Classification is based either on quantitative analysis of a limited data set of high-quality, 

published/accessible plots and/or plots from only part of the geographic range, or on a more qualitative 

assessment of published/accessible field data of sufficient quantity and quality.

A brief (1-2 paragraph) description of the range, structure, composition, environmental setting and dynamics 

associated with the Association. HTML is used to mark italics.

The Heritage Conservation Status Global Rank which best characterizes the relative rarity or endangerment of 

the Association worldwide. 

The Heritage Conservation Status Global Rank with qualifiers and ranges removed for easier interpretation.

The date the Global Rank was last reviewed.

Reasons that the Global Rank for the Association was assigned, including key ranking variables and other 

considerations used.

The two-letter postal codes for nations (countries) in which the Association occurs. When the occurrence is 

uncertain, a ? is appended.
The two-letter postal codes for U.S. states and Canadian provinces in which the Association occurs. Mexican 

two-letter state abbreviations are preceded by "MX". When the occurrence of the Association in a state/province 

is uncertain, a ? is appended.

List of TNC Conservation Ecoregion codes where the Association is thought to occur, listed with the 

Occurrence Status of the Association in each ecoregion. C = Confident or certain; P = Predicted or probable; ? 

= Possible; X = Presumed extirpated. See here for a map and more information: 

http://www.natureserve.org/explorer/eodist.htm#ecoregions.

List of USFS Ecoregion Codes, at Province, Section, or Subsection levels, where the Association is thought to 

occur, listed alpha-numerically with the Occurrence Status status at each ecoregion level. C = Confident or 

certain; P = Predicted or probable; ? = Possible; X = Presumed extirpated. Ecoregions follow Bailey et al. 

(1994) in the West and Keys et al. (1995) in the East. See here for a map and more information: 

http://www.natureserve.org/explorer/eodist.htm#ecoregions.

Short citations of all references used in documenting the classification/concept and characterization of this 

Association. The full citations are listed at the bottom of each Association's NatureServe Explorer report.