Skip to main content
Log in

Landscape Effects on Ecosystems: Birds as Active Vectors of Nutrient Transport to Fragmented Urban Forests Versus Forest-Dominated Landscapes

  • Published:
Ecosystems Aims and scope Submit manuscript

Abstract

In urban landscapes, nearby birds contribute to allochthonous nutrient flow from residential areas to fragmented forests by consuming food in residential areas and depositing feces in forests. To estimate allochthonous nutrient flow qualitatively, the stable nitrogen (δ15N) and carbon (δ13C) isotope approach is useful. However, the quantitative allochthonous flow rate cannot be estimated by the stable-isotope approach. To quantify allochthonous input, we compare two different landscapes. We assume that the input rate in deep forests in the forest-dominated landscape is the basic autochthonous flow that is common to various forests, and estimate the allochthonous nutrient input by subtracting the autochthonous flow from the total input in urban forests. The observed nutrient-input rate in the forest-dominated landscape as the autochthonous flow is 0.0298 kg P ha−1 y−1 and 0.319 kg N ha−1 y−1. Using these values, the allochthonous P input (kg P ha−1 y−1) is estimated at 0.0307 in urban fragmented forests and 2.31 in forests with crow roosts, whereas N input (kg N ha−1 y−1) is 0.397 in urban fragmented forests and 23.2 in forests with crow roosts. Our estimation shows that, in urban forests with roosts, birds contribute 2.7 times the amount of allochthonous P contributed via other pathways, and in urban forests without roosts they contribute 0.035 times the amount; and in addition, birds contribute 0.66 times the amount of allochthonous N input via other pathways in urban forests with crow roosts and 0.011 times the amount in urban forests without roosts. We also measure stable nitrogen and carbon isotope ratios, %N, %P, and %C to estimate the diet of birds. High δ15N and δ13C values in crow roosts indicate that they eat foods such as livestock meat, C4 maize, or fish. High avian biomass is the major reason for the large nutrient input in urban landscapes, especially in urban forests with crow roosts.

This is a preview of subscription content, log in via an institution to check access.

Access this article

Price excludes VAT (USA)
Tax calculation will be finalised during checkout.

Instant access to the full article PDF.

Figure 1
Figure 2
Figure 3
Figure 4

Similar content being viewed by others

References

  • Abe Y. 1989. Pollutant load from atmospheric deposition. In: Kunimatsu T, Muraoka K, editors. Modeling river pollution. Gihodo shuppan, Tokyo, Japan (in Japanese), pp 24–34.

    Google Scholar 

  • Bennett EM, Carpenter SR, Caraco NF. 2001. Human impact on erodable phosphorus and eutrophication: a global perspective. BioScience 51:227–234.

    Article  Google Scholar 

  • Boring LR, Swank WT, Waide JB, Henderson GS. 1988. Sources, fates, and impacts of nitrogen inputs to terrestrial ecosystems: review and synthesis. Biogeochemistry 6:119–159.

    Article  CAS  Google Scholar 

  • Falster DS, Warton DI, Wright IJ. 2006. SMATR: Standardised major axis tests and routines, ver 2.0. http://www.bio.mq.edu.au/ecology/SMATR/

  • Fujita M, Koike F. 2007. Birds transport nutrients to fragmented forests in an urban landscape. Ecological Applications 17:648–654.

    Article  PubMed  Google Scholar 

  • Fukami T, Wardle DA, Bellingham PJ, Mulder CPH, Towns DR, Yeates GW, Bonner KI, Durrett MS, Grant-Hoffman MN, Williamson WM. 2006. Above- and below-ground impacts of introduced predators in seabird-dominated island ecosystems. Ecology Letters 9:1299–1307.

    Article  PubMed  Google Scholar 

  • Ham YS, Tamiya S, Choi IS. 2006. Contribution of dissolved organic nitrogen deposition to nitrogen saturation in a forested mountainous watershed in Tsukui, Central Japan. Water, Air, and Soil Pollution. 178:113–120.

    Article  CAS  Google Scholar 

  • Hilderbrand GV, Hanley TA, Robbins CT, Schwartz CC. 1999. Role of brown bears (Ursus arctos) in the flow of marine nitrogen into a terrestrial ecosystem. Oecologia 121:546–550.

    Article  Google Scholar 

  • Hill MO. 1979. TWINSPAN – A FORTRAN program for arranging multivariate data in an ordered two-way table by classification of the individuals and attributes. Cornell University, Ithaca, NY, US.

    Google Scholar 

  • Hobara S, Koba K, Osono T, Tokuchi N, Ishida A, Kameda K. 2005. Nitrogen and phosphorus enrichment and balance in forests colonized by cormorants: Implications of the influence of soil adsorption. Plant and Soil 268:89–101.

    Article  CAS  Google Scholar 

  • Hobson KA, Clark RG. 1992. Assessing avian diets using stable isotopes. II: factors influencing diet–tissue fractionation. Condor 94:189–197.

    Article  Google Scholar 

  • Hobson KA, Piatt JF, Pitocchelli J. 1994. Using stable isotopes to determine seabird trophic relationships. Journal of Animal Ecology 63:786–798.

    Article  Google Scholar 

  • Jokimäki J, Suhonen J. 1998. Distribution and habitat selection of wintering birds in urban environments. Landscape and Urban Planning 39:253–263.

    Article  Google Scholar 

  • Kitchell JF, Schindler DE, Herwig BR, Post DM, Olson MH. 1999. Nutrient cycling at the landscape scale: The role of diel foraging migrations by geese at the Bosque del Apache National Wildlife Refuge, New Mexico. Limnology and Oceanography 44:828–836.

    Google Scholar 

  • Kiyosu Y. 1978. The birds of Japan I, II and III. Revised edn. Tokyo, Japan: Kodansha (in Japanese)

  • Kurosawa R, Matsuo T, Tokunaga T, Kobayashi T, Sato E. 2004. Breeding performances of crows in a park-like sites with rich vegetation in urban areas: A comparison between Sapporo and Tokyo. STRIX 22:109–116.

    Google Scholar 

  • Lim HC, Sodhi NS. 2004. Responses of avian guilds to urbanisation in a tropical city. Landscape and Urban Planning 66:199–215.

    Article  Google Scholar 

  • Lindeboom HJ. 1984. The nitrogen pathway in a penguin rookery. Ecology 65:269–277.

    Article  CAS  Google Scholar 

  • Long JL. 1981. Introduced birds of the world. Reed, Wellington.

    Google Scholar 

  • Marion L, Clergeau P, Brient L, Bertru G. 1994. The importance of avian-contributed nitrogen (N) and phosphorus (P) to Lake Grand-Lieu, France. Hydrobiologia 279–280:133–147.

    Article  Google Scholar 

  • Miyawaki A. 1976. The potential natural vegetation in prefecture Kanagawa. Japan: The Board of Education of the Kanagawa Prefecture (in Japanese)

    Google Scholar 

  • Morishita E, Itao K, Sasaki K, Higuchi H. 2003. Movements of crows in urban areas, based on PHS tracking. Global Environmental Research 7:181–191.

    Google Scholar 

  • Murphy J, Riley JP. 1962. A modified single solution method for the determination of phosphate in natural waters. Analytica Chimica Acta 27:31–36.

    Article  CAS  Google Scholar 

  • Nakamura T, Nakamura M. 1995. Bird’s life in Japan with color pictures. Birds of mountain, woodland and field. Hoikusha, Osaka, Japan (in Japanese).

    Google Scholar 

  • Natuhara Y, Imai C. 1996. Spatial structure of avifauna along urban–rural gradients. Ecological Research 11:1–9.

    Article  Google Scholar 

  • Newman EI. 1995. Phosphorus inputs to terrestrial ecosystems. J. Ecology 83:713–726.

    Article  Google Scholar 

  • Oliver JD, Legovic T. 1988. Okefenokee marshland before, during and after nutrient enrichment by a bird rookery. Ecological Modelling 43:195–223.

    Article  CAS  Google Scholar 

  • Rose MD, Polis GA. 1998. The distribution and abundance of coyotes: the effects of allochthonous food subsidies from the sea. Ecology 79:998–1007.

    Article  Google Scholar 

  • Rossi L, Costantini ML, Brilli M. 2007. Does stable isotope analysis separate transgenic and traditional corn (Zea mays L.) detritus and their consumers? Applied Soil Ecology 35:449–453.

    Article  Google Scholar 

  • Scharenbroch BC, Lloyd JE, Johnson-Maynard JL. 2005. Distinguishing urban soils with physical, chemical, and biological properties. Pedrobiologia 49: 283–296.

    Article  CAS  Google Scholar 

  • Schoeninger MJ, DeNiro MJ. 1984. Nitrogen and carbon isotopic composition of bone collagen from marine and terrestrial animals. Geochimica et Cosmochimica Acta 48:625–639.

    Article  CAS  Google Scholar 

  • Smith SV, Swaney DP, Talaue-McManus L, Bartley JD, Sandhey PT, McLaughlin CJ, Dupra VC, Crossland CJ, Buddemeier RW, Maxwell BA, Wulff F. 2003. Humans, hydrology, and the distribution of inorganic nutrient loading to the ocean. BioScience 53:235–245.

    Article  Google Scholar 

  • Sokal RR, Rohlf FJ. 1995. Biometry 3rd edn. WH Freeman and Company, NY, USA.

    Google Scholar 

  • Tilman D. 1982. Resource competition and community structure. Princeton University Press, Princeton, NJ.

    Google Scholar 

  • Tokeshi M. 1993. Species abundance patterns and community structure. Advances in Ecological Research 24:111–186.

    Article  Google Scholar 

  • Tsutsumi T. 1989. Forest Ecology. Asakura Shoten, Tokyo (in Japanese).

    Google Scholar 

  • Ueta M, Kurosawa R, Hamao S, Kawachi H, Higuchi H. 2003. Population change of jungle crows in Tokyo. Global Environmental Research 7:131–137.

    Google Scholar 

  • Vitousek PM, Aber JD, Howarth RW, Likens GE, Matson PA, Schindler DW, Schlesinger WH, Tilman DG. 1997. Human alteration of the global nitrogen cycle: sources and consequences. Ecological Applications 7:737–750.

    Google Scholar 

  • Wild Bird Society of Japan Kanagawa Chapter. 2002. Birds in Kanagawa in the 20th century: list of birds in Kanagawa 4. Yokohama: Wild Bird Society of Japan Kanagawa Chapter (in Japanese)

Download references

Acknowledgements

We thank Dr. Akiko Sakai, Dr. Nobuhiro Kaneko, and Dr. Ichiro Tayasu for their advice on this research. Analyses of CNP and stable isotopes were carried out in the Soil Ecology Research Group, Yokohama National University, and the Center for Ecological Research, Kyoto University, respectively. We thank FM Tsukui Farm, Tokyo University of Agriculture and Technology, for providing accommodation during the field survey. We thank Masayo Isozaki, Ryoko Tanaka, Miho Sato, Masakazu Dobata, Yoshiko Kobayashi, and Makiko Nagai for helping with fieldwork. The research was partly supported by the 21st century COE Program “Environmental Risk Management for Bio-Eco Systems.” This paper is also a part of the outcome of the JSPS Global COE Program (E-04): "In Search of Sustainable Humanosphere in Asia and Africa." The experiments comply with the current laws of the country in which they were performed. Finally, I thank Dr. Stephen J. Leisz for useful comments on the manuscript.

Author information

Authors and Affiliations

Authors

Corresponding author

Correspondence to Motoko Fujita.

Additional information

MF conceived and designed the study, performed research, analyzed data, and wrote the manuscript. FK helped conceive and design the study, data analysis, and assisted writing.

Electronic supplementary material

Below is the link to the electronic supplementary material.

(DOC 30 kb)

Rights and permissions

Reprints and permissions

About this article

Cite this article

Fujita, M., Koike, F. Landscape Effects on Ecosystems: Birds as Active Vectors of Nutrient Transport to Fragmented Urban Forests Versus Forest-Dominated Landscapes. Ecosystems 12, 391–400 (2009). https://doi.org/10.1007/s10021-009-9230-z

Download citation

  • Received:

  • Revised:

  • Accepted:

  • Published:

  • Issue Date:

  • DOI: https://doi.org/10.1007/s10021-009-9230-z

Keywords

Navigation