Hydrangea macrophylla (Thunb.) Ser.

Bigleaf hydrangea

Synonyms
  • Hortensia macrophylla (Thunb.) H.Ohba & S.Akiyama
  • Viburnum macrophyllum Thunb.
  • Hortensia japonica J.F.Gmel.
  • Hortensia macrophylla f. isobue (H.Ohba & S.Akiyama) H.Ohba & S.Akiyama
  • Hortensia macrophylla f. isonotaki (H.Ohba & S.Akiyama) H.Ohba & S.Akiyama
  • Hortensia macrophylla f. normalis (E.H.Wilson) H.Ohba & S.Akiyama
  • Hortensia mutabilis Schneev.
  • Hortensia nigra Carrière
  • Hortensia opuloides Lam.
  • Hortensia rosea Desf.
  • Hortensia speciosa Pers.
  • Hydrangea azisai Siebold
  • Hydrangea azisai var. foliis-aureovariegatis Siebold & Zucc.
  • Hydrangea cyanoclada G.Nicholson
  • Hydrangea florida Salisb.
  • Hydrangea hortensia Siebold
  • Hydrangea hortensia var. azisai (Siebold) A.Gray
  • Hydrangea hortensia var. macrosepala (Regel) Rehder
  • Hydrangea hortensia var. maculata (Blume) K.Koch
  • Hydrangea hortensia var. mariesii Bean
  • Hydrangea hortensia var. otaksa (Siebold & Zucc.) A.Gray
  • Hydrangea hortensia f. otaksa (Siebold & Zucc.) Franch. & Sav.
  • Hydrangea hortensia f. rosea Bean
  • Hydrangea hortensia var. rosea (Bean) J.H.Veitch
  • Hydrangea hortensia f. variegata (E.J.Lowe & W.Howard) G.Nicholson
  • Hydrangea hortensis Sm.
  • Hydrangea hortensis var. alba H.B.May
  • Hydrangea hortensis var. maculata Blume
  • Hydrangea hortensis var. mariesii (Bean) Bean
  • Hydrangea japonica var. albovariegatis Van Houtte
  • Hydrangea japonica var. coerulescens Regel
  • Hydrangea japonica fimbriata-macrophylla Jacob-Makoy
  • Hydrangea japonica var. foliis-variegatis André
  • Hydrangea japonica f. hortensia Regel
  • Hydrangea japonica var. macrosepala Regel
  • Hydrangea japonica var. otaksa Regel
  • Hydrangea japonica var. plena Regel
  • Hydrangea japonica speciosa Hovey
  • Hydrangea japonica var. variegata (E.J.Lowe & W.Howard) Regel
  • Hydrangea japonica variegata E.J.Lowe & W.Howard
  • Hydrangea macrocephala Dippel
  • Hydrangea macrophylla f. azisai (Siebold) E.H.Wilson
  • Hydrangea macrophylla f. caesia Nakai
  • Hydrangea macrophylla var. hattoriana Kitam.
  • Hydrangea macrophylla f. hortensia (Regel) Rehder
  • Hydrangea macrophylla var. hortensis (Sm.) Rehder
  • Hydrangea macrophylla f. isobue H.Ohba & S.Akiyama
  • Hydrangea macrophylla f. isonotaki H.Ohba & S.Akiyama
  • Hydrangea macrophylla f. leucantha Makino
  • Hydrangea macrophylla f. macrosepala (Regel) E.H.Wilson
  • Hydrangea macrophylla f. maculata (Blume) E.H.Wilson
  • Hydrangea macrophylla f. mandschurica (Dieck) E.H.Wilson
  • Hydrangea macrophylla f. mariesii (Bean) E.H.Wilson
  • Hydrangea macrophylla var. normalis E.H.Wilson
  • Hydrangea macrophylla f. normalis (E.H.Wilson) H.Hara
  • Hydrangea macrophylla f. nuda Konta & S.Matsumoto
  • Hydrangea macrophylla f. otaksa (Siebold & Zucc.) E.H.Wilson
  • Hydrangea macrophylla var. otaksa (Siebold & Zucc.) Honda
  • Hydrangea macrophylla f. veitchii E.H.Wilson
  • Hydrangea mandshurica Dippel
  • Hydrangea maritima Haw.-Booth
  • Hydrangea mutabilis Steud.
  • Hydrangea nigra Dippel
  • Hydrangea opuloides (Lam.) K.Koch
  • Hydrangea opuloides var. azisai (Siebold) Dippel
  • Hydrangea opuloides var. hortensia Dippel
  • Hydrangea opuloides var. japonica C.K.Schneid.
  • Hydrangea opuloides f. macrosepala (Regel) Dippel
  • Hydrangea opuloides var. mandschurica Dieck
  • Hydrangea opuloides var. mariesii (Bean) Rehder
  • Hydrangea opuloides var. otaksa (Siebold & Zucc.) Dippel
  • Hydrangea opuloides var. plena Rehder
  • Hydrangea opuloides var. variegata (E.J.Lowe & W.Howard) Rehder
  • Hydrangea otaksa Siebold & Zucc.
  • Hydrangea sieboldii Dippel
  • Hydrangea sinensis Dippel
  • Macnemaraea opulina P.Willemet
  • Primula mutabilis Lour.

Introduction

Bigleaf hydrangea, Hydrangea macrophylla, is a large deciduous woody shrub endemic in the wild to a comparatively restricted part of Japan but transformed through centuries of cultivation into one of the world's most familiar ornamental shrubs. Wild plants occur principally along the warm Pacific coast of central Japan, including the Bōsō, Miura, and Izu peninsulas, the Izu Islands, and parts of the Ogasawara island system. They commonly reach about 2–3 m and typically have broad, thick, glossy, essentially glabrous leaves, contrasting with the smaller stature, thinner and usually hairier foliage, and predominantly montane ecology of H. serrata.

Section Macrophyllae underwent a major reinterpretation when Murakami et al. (2024) sampled 93 wild populations across the Japanese distribution of the complex and analyzed thousands of genome-wide SNPs. Their trees divided the section into two deeply supported principal lineages. One contains H. serrata, H. acuminata, and H. minamitanii; the other contains H. macrophylla and H. yesoensis, with each species forming its own fully supported genomic lineage. The split between the two major branches was estimated at approximately 2.49 million years ago, suggesting that repeated Pleistocene climatic isolation contributed substantially to the modern diversity of the section.

The resulting relationship is striking. The closest major sectional relative of warm-coastal H. macrophylla is not ordinary mountain hydrangea but the much more northerly H. yesoensis. Their shared ancestry is therefore older than the modern ecological contrast between a salt-exposed southern coastal shrub and a northern temperate-forest hydrangea. That distinction helps explain why superficial ecology alone previously obscured the deeper structure of the group.

Wild H. macrophylla is considerably more ecologically specialized than the familiar garden plant suggests. Morimoto et al. (2024) found that many natural populations occupy coastal sites exposed to strong sea-salt aerosols and soils with elevated salinity. Leaf-cation evidence indicates an ability to regulate sodium allocation while tolerating relatively high sodium concentrations. Other island populations extend inland into mountain vegetation, where plants may develop thinner, less glossy leaves and occasional trichomes, approaching some features more typical of H. serrata. Still others occupy nutrient-poor rocky surfaces or volcanic scoria, and individuals have even been documented growing epiphyte-like on trunks of Cyathea tree ferns. These observations portray H. macrophylla not as a horticultural artifact but as an ecologically flexible coastal-island species with substantial natural phenotypic variation.

The boundary with H. serrata is nevertheless permeable. Uemachi et al. (2026) analyzed 320 plants from the macrophylla distributional region and detected evidence of natural hybridization in many populations on the Bōsō and Izu peninsulas, while finding little evidence of recent hybridization in the four sampled Izu Islands. Genome-wide evidence still supports macrophylla and serrata as distinct evolutionary lineages, so Tree TSAR interprets these populations as secondary contact between distinct species rather than evidence that the species boundary disappears.

The enormous nomenclatural history of H. macrophylla reflects horticulture at least as much as wild taxonomic diversity. POWO currently records 78 synonyms, including names based on different inflorescence forms, flower colors, variegation patterns, and cultivated selections. The ordinary wild inflorescence is lacecap-like, with fertile central flowers surrounded by enlarged showy marginal flowers. Mophead or temari plants bear inflorescences dominated by enlarged showy flowers. Although such plants became emblematic of cultivation, genetic analysis of naturally occurring mophead individuals at Jogasaki on the Izu Peninsula indicates that the phenotype can arise and persist within wild populations. Horticulture therefore amplified natural developmental variation rather than necessarily inventing the underlying floral architecture.

Horticultural and Agricultural Uses

Few woody plants have had a larger ornamental impact than H. macrophylla. It underlies an immense diversity of lacecap and mophead cultivars grown as landscape shrubs, container plants, greenhouse crops, and cut flowers. Its large inflorescences and capacity for blue, purple, pink, red, or intermediate sepal coloration have made it the horticultural archetype of Hydrangea. The famous color response is chemically associated with anthocyanins, copigments, aluminum availability, and soil conditions rather than representing fixed taxonomic variation.

Modern breeding has repeatedly crossed H. macrophylla with H. serrata and other hydrangeas to introduce cold hardiness, altered architecture, reblooming, flower morphology, and novel coloration. Yet the cultivated gene pool represents only part of the diversity available in wild Japanese populations. Earlier molecular work noted that many European-derived cultivars trace to a comparatively limited set of introductions, making wild macrophylla and allied species especially important breeding resources.

Wild coastal populations may also contain useful genetic resources for landscape plants exposed to salt spray or saline soils. The physiological work of Morimoto et al. demonstrates that the native ecology of the species already includes environments stressful to many ornamental shrubs, giving wild provenance material potential practical importance beyond ornamental novelty.

Conservation Concerns

The abundance of bigleaf hydrangea in gardens can obscure how geographically restricted the wild species actually is. Natural populations are concentrated in a relatively small portion of Japan, particularly the three Pacific peninsulas and associated island systems. Kew's automated extinction-risk model predicts the species to be not threatened, but this is a model-based prediction rather than a formal IUCN assessment.

Conservation should focus on preserving the geographic and ecological diversity of wild populations rather than merely maintaining cultivated representatives. Coastal populations, inland island populations, volcanic-substrate populations, and isolated island gene pools may represent substantially different adaptive resources. The unusual wild mophead population at Jogasaki is itself a conservation-worthy genetic resource because it demonstrates naturally occurring developmental variation otherwise associated primarily with horticulture.

Natural hybridization is an additional conservation consideration. Uemachi et al. (2026) explicitly conclude that protection of H. macrophylla genetic resources on the Bōsō and Izu peninsulas requires attention not only to declining or fragmented populations but also to introgression from H. serrata. Hybridization is a natural evolutionary process and should not automatically be treated as degradation, but conserving relatively unintrogressed island populations alongside contact-zone populations would preserve a broader representation of the species' evolutionary history.

Additional Information

References and Further Reading

Morimoto H, Harada S, Shukuya S, Yamamoto S, Handa T (2024) Distribution, ecology, and adaptation to salinity stress of wild Hydrangea macrophylla endemic to Japan. Plant Ecology 225(8): 775–790. https://doi.org/10.1007/s11258-024-01433-6 (opens in a new tab)

Murakami S, Ito T, Uemachi T, Fujii S, Matsuo A, Suyama Y, Maki M (2024) Phylogenetic relationships and divergence time of Hydrangea sect. Macrophyllae (Hydrangeaceae) revealed by genome-wide SNPs. Plant Systematics and Evolution 310(4): 27. https://doi.org/10.1007/s00606-024-01902-5 (opens in a new tab)

Uemachi T, Mizuhara Y, Deguchi K, Shinjo Y, Kajino E, Ohba H (2014) Phylogenetic relationship of Hydrangea macrophylla (Thunb.) Ser. and H. serrata (Thunb.) Ser. evaluated using RAPD markers and plastid DNA sequences. Journal of the Japanese Society for Horticultural Science 83(2): 163–171. https://doi.org/10.2503/jjshs1.CH-092 (opens in a new tab)

Uemachi T, Tojo N, Hayashi Y, Kinoshita M, Shibata A, Kondo Y, Iwasawa H (2026) Genetic conservation of endemic Hydrangea macrophylla: Assessing natural hybridization with H. serrata using ITS sequences of nuclear ribosomal DNA. The Horticulture Journal 95(2): 285–297. https://doi.org/10.2503/hortj.SZD-094 (opens in a new tab)