Submitted by Jos? Henrique Henrique (jose.neves@ufvjm.edu.br) on 2017-12-18T18:25:58Z No. of bitstreams: 2 license_rdf: 0 bytes, checksum: d41d8cd98f00b204e9800998ecf8427e (MD5) mariana_generoso_ferreira.pdf: 1487910 bytes, checksum: 5d8038ca69034b764ba796a3a18d0907 (MD5) / Approved for entry into archive by Rodrigo Martins Cruz (rodrigo.cruz@ufvjm.edu.br) on 2018-01-03T17:13:11Z (GMT) No. of bitstreams: 2 license_rdf: 0 bytes, checksum: d41d8cd98f00b204e9800998ecf8427e (MD5) mariana_generoso_ferreira.pdf: 1487910 bytes, checksum: 5d8038ca69034b764ba796a3a18d0907 (MD5) / Made available in DSpace on 2018-01-03T17:13:11Z (GMT). No. of bitstreams: 2 license_rdf: 0 bytes, checksum: d41d8cd98f00b204e9800998ecf8427e (MD5) mariana_generoso_ferreira.pdf: 1487910 bytes, checksum: 5d8038ca69034b764ba796a3a18d0907 (MD5) Previous issue date: 2017 / O agricultor deve adequar-se ?s exig?ncias da nova legisla??o ambiental brasileira, quanto ? recupera??o de ?reas de preserva??o permanente e reserva legal. Um dos problemas que o produtor pode enfrentar ? a recupera??o de ?reas degradadas, que podem conter, entre outros contaminantes, res?duos de herbicidas. O 2,4-D e picloram s?o herbicidas hormonais mimetizadores de auxina. Entre os grupos vegetais, as esp?cies das matas ciliares t?m sido pouco relatadas quanto aos efeitos de res?duos desses herbicidas no ambiente. As an?lises micromorfol?gicas e micromorfom?tricas s?o ferramentas importantes no aux?lio do diagn?stico precoce da inj?ria, visto que modifica??es vis?veis podem aparecer em fase tardia da intoxica??o. Objetivou-se com este trabalho avaliar o desenvolvimento inicial de dez esp?cies arb?reas em substrato com res?duos da mistura de herbicidas 2,4-D+picloram e verificar os efeitos nas modifica??es anat?micas foliares de Mabea fistulifera e Zeyheria tuberculosa. Em delineamento em blocos ao acaso com tr?s repeti??es, foram distribu?dos 40 tratamentos em esquema fatorial 4x10. O primeiro fator foi composto por quatro doses da mistura comercial de 2,4-D+picloram correspondentes a 0,00; 0,166; 0,333 e 0,666 g ha-1 (Tordon?, contendo 240 g de 2,4-D e 64 g de picloram por litro). O segundo fator foi composto por dez esp?cies arb?reas: Machaerium opacum Vogel, Machaerium nyctitans (Vell.) Benth., Cassia ferruginea (Schrad.) Schrad. ex DC., Senna macranthera (DC. ex. Collad.) H.S. Irwin e Barnaby, Anadenanthera colubrina (Vell.), Brenan, Senegalia polyphylla (DC.) Britton e Rose, Piptadenia gonoacantha (Mart.) J.F. Macbr., Dalbergia villosa (Benth.) Benth., Mabea fistulifera Mart. e Zeyheria tuberculosa (Vell) Bureau ex Verl. Avalia??es morfol?gicas e anat?micas em plantas jovens foram realizadas conforme a metodologia padr?o. Para as vari?veis morfol?gicas das dez esp?cies arb?reas foram avaliados: intoxica??o, sobreviv?ncia, altura das pl?ntulas, n?mero de folhas, ?rea foliar, massa seca da parte a?rea e da raiz, di?metro do caule, o volume da raiz, o ?ndice de velocidade de emerg?ncia e a emerg?ncia. Por meio de avalia??es micromorfom?tricas foram medidas, na sec??o transversal das folhas de Mabea fistulifera e Zeyheria tuberculosa, a espessura dos tecidos, a epiderme adaxial e abaxial, par?nquima pali??dico e lacunoso, al?m da l?mina total. Para a ?rea foliar foram realizadas fotografias das folhas e mensuradas com aux?lio do software Image K. As esp?cies arb?reas sobreviveram ? aplica??o do produto, com varia??o na sensibilidade. Os res?duos da mistura dos herbicidas prejudicaram a maioria das esp?cies testadas em rela??o ?s avalia??es do desenvolvimento inicial. M. fistulifera, P. gonoacantha e Z. tuberculosa apresentaram maior toler?ncia ? mistura de herbicidas. Em rela??o ? anatomia e ?rea foliar, de maneira geral, a esp?cie Z. tuberculosa foi afetada negativamente pelos herbicidas. M. fistulifera se mostrou mais tolerante ? presen?a dos contaminantes. / Disserta??o (Mestrado) ? Programa de P?s-Gradua??o em Ci?ncia Florestal, Universidade Federal dos Vales do Jequitinhonha e Mucuri, 2017. / The farmer must adapt to the requirements of the new brazilian environmental legislation, regarding the recovery of permanent preservation areas and legal reserve. One of the problems that the producer may face is the recovery of degraded areas, which may contain, among other contaminants, herbicide residues. 2,4-D and picloram are auxin mimicking hormonal herbicides. Among the plant groups, the species of the riparian forests have been little reported as to the effects of residues of these herbicides on the environment. Micromorphological and micromorphometric analyzes are important tools to aid in the early diagnosis of injury, since visible changes may appear in the later stages of intoxication. The objective of this work was to evaluate the initial development of ten substrate tree species with residues from of the 2,4-D + picloram herbicide mixture and to verify the effects on the anatomical modifications of Mabea fistulifera and Zeyheria tuberculosa. In a randomized block design with three replicates, 40 treatments were distributed in a 4x10 factorial scheme. The first factor was composed of four doses of the commercial mixture of 2,4-D + picloram corresponding to 0,00; 0,166; 0,336 and 0,666 g ha-1 (Tordon?, containing 240 g of 2,4-D and 64 g of picloram per liter). The second factor was composed of ten tree species: Machaerium opacum Vogel, Machaerium nyctitans (Vell.) Benth., Cassia ferruginea (Schrad.) Schrad. ex DC., Senna macranthera (DC. ex. Collad.) H.S. Irwin e Barnaby, Anadenanthera colubrina (Vell.), Brenan, Senegalia polyphylla (DC.) Britton e Rose, Piptadenia gonoacantha (Mart.) J.F. Macbr., Dalbergia villosa (Benth.) Benth., Mabea fistulifera Mart. and Zeyheria tuberculosa (Vell) Bureau ex Verl. Morphological and anatomical evaluations in young plants were performed according to the standard methodology. For the morphological variables of the ten tree species were evaluated: intoxication, survival, seedling height, number of leaves, leaf area, dry mass of shoot and root, stem diameter, root volume, emergency speed index and emergency. Through micromorphometric evaluations, tissue thickness, adaxial and abaxial epidermis, pali?adic and lacunacetic parenchyma were measured, in the cross section of the leaves of Mabea fistulifera and Zeyheria tuberculosa, in addition to the total lamina. For leaf area, leaf photographs were taken and measured using Image K software. Tree species survived the application of the product, with variation in sensitivity. Residues of the herbicide mixture adversely affected most of the tested species in relation to initial developmental assessments. M. fistulifera, P. gonoacantha and Z. tuberculosa presented greater tolerance to the herbicide mixture. In relation to the anatomy and leaf area, in general, the species Z. tuberculosa was negatively affected by the herbicides. M. fistulifera was more tolerant to the presence of contaminants.