Urban soil characteristics and limitations for landscape planting in Hong Kong

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Abstract

Soils in urban areas have not received adequate attention in relation to landscape planting. Recent urban tree surveys in Hong Kong identified many arboricultural problems related to stressful habitat conditions including edaphic ones. Soil constraints in the crowded city are acute and yet relevant data are lacking. This project evaluated in the field and laboratory 100 soil samples obtained from sites of varied natural and disturbance history at difficult roadside tree-pit sites in urban Hong Kong. An extensive range of physical and chemical properties were assessed to establish baseline information on soil limitations to amenity-vegetation growth. Most soils have lost natural soil horizons with morphological features of fill materials such as poor structure and artificial layering. They are excessively stony and coarse-textured, with abundance of building rubble and other foreign substances. The extensive soil compaction, associated with structural degradation and loss of porosity, is inimical to aeration, drainage, storage of plant-available moisture, and root growth. Release of carbonate from the calcareous construction waste has induced alkaline pH, with consequences on micronutrient and phosphorus deficiency. Organic matter contents, and the related supply of essential nitrogen and phosphorus, are all meager. The capacity to hold nutrient bases and the amount held in available forms are both inadequate for vigorous plant performance. There are signs of pollution by heavy metals, especially lead, which are derived from air-borne sources related to vehicular traffic. The results help to ascertain the need for soil tests in landscaping endeavors, to reinforce a weak link in landscaping programs, to establish a package of recommendations to improve urban soil management, to enhance the cost-effectiveness of greening programs, and to augment urban-tree performance so as to reduce recurrent management liability and burden.

Introduction

Trees in cities can be considered an anathema, for as natural objects they have to live in an overwhelmingly artificial habitat. They are beset by many subaerial and subterranean stresses (Grey and Deneke, 1986; Miller, 1988; Bradshaw et al., 1995). Urban tree management, an applied aspect of urban ecology, is a continual attempt to mediate between the two interacting if not conflicting components. Most city trees have a life-span much shorter than their biological potentials (Gilbertson and Bradshaw, 1985; Insley and Buckley, 1986) with growth in a constant state of turmoil. Urban trees in Hong Kong, with an exceptionally high-density development, poor environmental quality, and frequent construction damages, have to struggle to survive (Jim, 1986a, Jim, 1987a). Recent city-wide surveys of street trees verified widespread poor performance (Jim, 1994, Jim, 1996a).

Poor site condition is the main cause of unhealthy urban trees (Jim, 1992, Jim, 1997a, Jim, 1997b). Urban soil researches conducted elsewhere confirm the severe constraints imposed by inadequacies and obstacles in the subsurface environment (summarized in Bullock and Gregory, 1991; Craul, 1992; Watson and Neely, 1994). Unfortunately, the soil is out of sight and difficult as well as expensive to assess using conventional means (Watson, 1994). It is too often taken for granted if not neglected altogether (Roberts and Roberts, 1986; Patterson, 1990). Urban arboriculture and horticulture practice has meager objective and empirical data to make sound judgements or recommendations. As a surrogate, the vast quantity of information and experience in agriculture and forestry has had to be borrowed, but the extrapolation can become far-fetched if not untenable.

Field evaluation of urban soils in an extensive range of sites in Hong Kong attest a notoriously difficult medium for vegetation growth. They are commonly limited by abundant underground utility lines (pipes and cables). Stones, boulders, construction rubbles, mortar, bricks, old paving, old and extant foundations, and other rather immutable obstructions, often frustrate planting efforts and render many sites unusable. Compacted surface and subsurface soil layers, frequently encountered, are restrictive to root spread and compromise the free movement of air and water. Less tangible chemical restrictions are widespread. Local tree planting practice, however, pays only lip service to the distressful state of urban soils, with little attempt to ameliorate the maladies or to replace them with better materials.

The municipal authority is implementing an ambitious planting programme. The last tree survey (Jim, 1994) found some 12,000 sites for new street trees in Hong Kong. Further urban expansion and urban renewal will provide more planting niches. If these new sites are treated in the same old way, similar mistakes of poor soil will be repeated. In time, the young trees will follow the same path as their predecessors and endure a life of hardship. Of the different urban soils (Blume, 1989; Hollis, 1991), the roadside ones are the most restrictive for plant growth (Barlett Tree Expert, 1968; Evans et al., 1990), yet they are expected to support linear tree belts with significant cityscape impacts. The lack of scientific information on urban soils is a serious impediment to the bold landscaping effort to enliven the otherwise drab city milieu. A better understanding of this fundamental resource base can enhance the cost-effectiveness of urban-tree programmes and reduce tree-management burdens.

This study evaluates the physical and chemical properties of urban soils in Hong Kong, with an emphasis on tree growth, through field assessment and laboratory analysis. The major soil limitations could be identified and remedied. As urban soil research has been largely ignored by soil scientists, empirical data have to be acquired at first hand. This study therefore attempts to encompass a wide range of soil properties, with a view to contributing objective-empirical information. It is hoped that the baseline findings can provide practical hints on soil management, namely to prescribe ameliorative measures in the form of physical manipulation, to add soil amendments, and to determine the need to replace site soils in extreme situations. Due to a lack of relevant systematic information, the study encompasses a large number of samples to cover a broad spectrum of site conditions.

Section snippets

Study area and methods

The research concentrates on soils at roadside habitats in urban Hong Kong. The target study area covered the old city core around the harbor with an inordinately high-density development and stressful environment. A total of 85 tree pits were excavated at 25 locations, all situated at pavement locations in developed neighborhoods. The concrete paving had to be removed before a pit could be excavated. Most pits measured about 1 m×1 m×1 m, but some were smaller due to obstructions such as

Field morphology

Natural pedological horizons are conspicuously absent. Surface organic (O) and mineral-organic (A) horizons cannot be found. In the subsoil, no discernible eluvial (E) or illuvial (B) subsurface horizons can be identified. Instead, distinctive artificial layering is common, denoting marked batch differences in composition. Most soils suffer from compaction, originated from sequential dumping of fill materials with variations in color, texture, structure, composition and contents of stones and

Soil reaction

The release of alkaline leachate from calcareous construction wastes can raise soil pH beyond the normal tolerance range of local humid-tropical landscape plants, and induce nutrient imbalance. Urban soils with alkaline reaction is common (Sukopp et al., 1979; Craul and Klein, 1980; Kelsey, 1994). The samples have a mean pH of 8.68 (mode 8.7, minimum 6.77, maximum 9.95), ranging from slightly to very strongly alkaline (Table 1, Fig. 3). Only one sample drops below neutrality; all the rest are

Management recommendations

Many urban-soil maladies are due to inadequacies in physical composition and properties, such as excessively sandy texture, too much stones and building debris, weakly-developed and easily degraded structure, and compaction. Poor-quality earth, often no better than construction wastes, should not have been dumped indiscriminately at future planting sites. They should be removed from designated planting sites. Thorough site survey with field assessment and laboratory soil tests should be

Implications and conclusion

Soil conservation work often stops at the city limit, and cities are simply labeled `urban' on soil maps (Spirn, 1992). City and nature too often have been treated as something antithetical and nonconformable. Urban horticulture for too long had had existed as though in an entirely different world. Yet, the fundamental requirements of optimal plant growth are the same for natural or human-modified soils, for they do not recognize artificial city–countryside boundaries. Too often, soil

Acknowledgements

I would like to take this opportunity to thank the Croucher Foundation and the Environment and Conservation Fund for research grant supports to conduct this study on urban soils in Hong Kong. The assistance in the field and laboratory by Mr. Samson Yip and Ms. Jeannette Liu of the University of Hong Kong, and the help in various ways by Mr. Lawrence Cheung and Mr. Lim-cho Choi of the Urban Services Department, are gratefully appreciated.

References (88)

  • G.B. Bodman et al.

    Influence of particle size distribution in soil compaction

    Hilgardia

    (1965)
  • Bolt, G.H., Koenigs, F.F.R., 1972. Physical and chemical aspects of the stability of soil aggregates. In: De Boodt, M....
  • Bradshaw, A.D., Hunt, B., Walmsley, T. (Eds.), 1995. Trees in the Urban Landscape: Principles and Practice. Spon,...
  • Bremner, J.M., Mulvaney, C.S., 1982. Nitrogen-total. In: Page, A.L., Miller, R.H., Keeney, D.R. (Eds.), Methods of Soil...
  • Bridges, E.M., 1991. Waste materials in urban soils. In: Bullock, P., Gregory, P.J. (Eds.), Soils in the Urban...
  • Bullock, P., Gregory, P.J. (Eds.), 1991. Soils in the Urban Environment. Blackwell, Oxford, 174...
  • Chancellor, W.J., 1971. Effects of compaction on soil strength. In: Barnes, K.K., Carleton, W.M., Taylor, H.M.,...
  • P.J. Craul

    A description of urban soils and their desired characteristics

    J. Arboriculture

    (1985)
  • Craul, P.J., 1992. Urban Soil in Landscape Design. Wiley, New York, NY, 396...
  • Craul, P.J., Klein, C.J., 1980. Characterisation of streetside soils in Syracuse NY. Metropolitan Tree Improvement...
  • M.N. Evans et al.

    Sidewalk design

    Landscape Architecture

    (1990)
  • R.R. Foil et al.

    The establishment and growth of loblolly pine seedlings on compacted soils

    Soil Sci. Soc. Am. Proc.

    (1967)
  • W. Fraedrich et al.

    Wood chip mulching around maples: effect on tree growth and soil characteristics

    J. Arboriculture

    (1982)
  • Gee, G.W., Bauder, J.W., 1986. Particle-size analysis. In: Klute, A. (Ed.), Methods of Soil Analysis, Part 1: Physical...
  • P. Gilbertson et al.

    Tree survival in cities: the extent and nature of the problem

    Arboricultural J.

    (1985)
  • E.F. Gilman

    Tree root spread in relation to branch dripline and harvestable root ball

    HortScience

    (1988)
  • E.F. Gilman

    Predicting root spread from trunk diameter and branch spread

    J. Arboriculture

    (1989)
  • J. Grabosky et al.

    A new urban tree soil to safely increase rooting volumes under sidewalks

    J. Arboriculture

    (1995)
  • J. Grabosky et al.

    Testing of structural urban tree soil materials for use under pavement to increase street tree rooting volumes

    J. Arboriculture

    (1996)
  • Gray, D.H., 1972. Soil and the city. In: Detwyler, T.R., Marcus, M.G. (Eds.), Urbanisation and Environment: The...
  • Grey, G.W., Deneke, F.J., 1986. Urban Forestry, 2nd edn. Wiley, New York, NY, 299...
  • C.G. Gunnerson

    Debris accumulation in ancient and modern cities

    J. Environ. Eng. Div., Am. Soc. Civil Eng.

    (1973)
  • Hamada, R., 1973. Urban ecosystem and soil. In: Numata, M. (Ed.), Fundamental Studies in the Characteristics of Urban...
  • M.O. Harrell et al.

    Pin oaks and silver maples chlorosis treatment with ferric ammonium citrate solution

    J. Arboriculture

    (1988)
  • Harris, W.L., 1971. The soil compaction process. In: Barnes, K.K., Carleton, W.M., Taylor, H.M., Throckmorton, R.I.,...
  • Harris, R.W., Paul, J.L., Leiser, A.T., 1977. Fertilizing Woody Plants. Leaflet 2958, Division of Agricultural...
  • P. Heilman

    Root penetration of Douglas-fir seedlings into compacted soil

    Forest Sci.

    (1981)
  • S.J. Hodge

    The effect of seven organic amendments on planting pit soil and tree performance

    Arboricultural J.

    (1995)
  • Hodgson, J.M. (Ed.), 1974. Soil Survey Field Handbook: Describing and Sampling Soil Profiles. Rothamsted Experimental...
  • Hollis, J.M., 1991. The classification of soils in urban areas. In: Bullock, P., Gregory, P.J. (Eds.), Soils in the...
  • Hollis, J.M., 1992. Proposals for the Classification, Description and Mapping of Soils in Urban Areas. English Nature,...
  • Insley, H., Buckley, G.P., 1986. Causes and prevention of establishment failure in amenity trees. In: Bradshaw, A.D.,...
  • Jim, C.Y., 1986a. Urban Tree Survey 1985: Pavement Trees Managed by the Urban Council. Urban Council, Hong Kong, 84...
  • C.Y. Jim

    Trampling impacts of recreationists on picnic sites in a Hong Kong country park

    Environ. Conserv.

    (1987)
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