Difficulties in using land use pressure and soil quality indicators to predict water quality

被引:4
作者
McDowell, Richard W. [1 ,2 ]
McNeill, Stephen J. [3 ]
Drewry, John J. [4 ]
Law, Richard [5 ]
Stevenson, Bryan [6 ]
机构
[1] Lincoln Univ, Fac Agr & Life Sci, POB 84, Christchurch 7647, New Zealand
[2] AgResearch, 19 Ellesmere Junct Rd, Lincoln 7608, New Zealand
[3] Manaaki Whenua Landcare Res, Informat, Gerald St Box 40, Lincoln 7640, New Zealand
[4] Manaaki Whenua Landcare Res, Soils & Landscapes, Private Bag 11052, Palmerston North, New Zealand
[5] Manaaki Whenua Landcare Res, Informat, Private Bag 11052, Palmerston North, New Zealand
[6] Manaaki Whenua Landcare Res, Land Use & Ecosyst, Hamilton 3127, New Zealand
关键词
E; coli; Land value; Nitrogen; Phosphorus; Stocking rate; NEW-ZEALAND; LEACHING LOSSES; PHOSPHORUS LOADS; CATCHMENT; RIVERS; MANAGEMENT; SEDIMENT; NITROGEN; NITRATE; CONSEQUENCES;
D O I
10.1016/j.scitotenv.2024.173445
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Intensive agriculture can impair river water quality. Soil quality monitoring has been used to measure the effect of land use intensification on water quality at a point and field scales but not at the catchment scale. Other farm scale land use pressures, like stocking rate and the value of land, which relate to land use intensity are now publicly available, nationally. We therefore tested whether point scale soil quality measures, together with newly available farm scale land use pressures (land valuation and stocking rate) and existing catchment and climatic characteristics could help predict the behaviour of water quality data across 192 catchments in New Zealand. We used a generalised additive model to make predictions of the change in nitrogen fractions ( r 2 = 0.65 - 0.71), phosphorus fractions ( r 2 = 0.51 - 0.70), clarity and turbidity ( r 2 = 0.42 - 0.46), and E. coli ( r 2 = 0.35) over 15 years. The state and trend of water quality was strongly related to a refined farm scale land use classification, and of (2024) to catchment and climatic characteristics (e.g. slope, elevation, and rainfall). Relationships with point scale soil quality measures and the land use pressures were weak. The weak relationship with land use pressures may be caused by using a single snapshot in time (2022), which cannot account for lag times in water quality response but leaves room for additional temporal data to improve predictive power. The weak relationship to soil quality measures was probably caused by limited data points ( n = 667 sites) that were unrepresentative of land use, and areas of catchment subject to processes like runoff or leaching. While national soil quality measures might be useful for evaluating environmental risk at the field or farm scale, without a large increase in sampling, they were not relevant at the catchment scale. Additional analyses should be performed to determine how many samples would be needed to detect a change using an environmentally focused soil test that can guide water quality management.
引用
收藏
页数:14
相关论文
共 87 条
[1]  
[Anonymous], 1993, Soil and Water Quality: an Agenda for Agriculture, DOI DOI 10.17226/2132
[2]   Identifying critical limits for soil quality indicators in agro-ecosystems [J].
Arshad, MA ;
Martin, S .
AGRICULTURE ECOSYSTEMS & ENVIRONMENT, 2002, 88 (02) :153-160
[3]  
Banasik K, 2014, IAHS-AISH P, V367, P163
[4]   Effects of Hydrology and Field Management on Phosphorus Transport in Surface Runoff [J].
Buda, Anthony R. ;
Kleinman, Peter J. A. ;
Srinivasan, M. S. ;
Bryant, Ray B. ;
Feyereisen, Gary W. .
JOURNAL OF ENVIRONMENTAL QUALITY, 2009, 38 (06) :2273-2284
[5]   Soil quality - A critical review [J].
Bunemann, Else K. ;
Bongiorno, Giulia ;
Bai, Zhanguo ;
Creamer, Rachel E. ;
De Deyn, Gerlinde ;
de Goede, Ron ;
Fleskens, Luuk ;
Geissen, Violette ;
Kuyper, Thom W. ;
Mader, Paul ;
Pulleman, Mirjam ;
Sukkel, Wijnand ;
van Groenigen, Jan Willem ;
Brussaard, Lijbert .
SOIL BIOLOGY & BIOCHEMISTRY, 2018, 120 :105-125
[6]   A new method to treat farm dairy effluent to produce clarified water for recycling and to reduce environmental risks from the land application of effluent [J].
Cameron, Keith C. ;
Di, Hong J. .
JOURNAL OF SOILS AND SEDIMENTS, 2019, 19 (05) :2290-2302
[7]   Land use disturbance indicators and water quality variability in the Biscayne Bay Watershed, Florida [J].
Carey, Richard O. ;
Migliaccio, Kati W. ;
Li, Yuncong ;
Schaffer, Bruce ;
Kiker, Gregory A. ;
Brown, Mark T. .
ECOLOGICAL INDICATORS, 2011, 11 (05) :1093-1104
[8]   The influence of landscape spatial configuration on nitrogen and phosphorus exports in agricultural catchments [J].
Casquin, Antoine ;
Dupas, Remi ;
Gu, Sen ;
Couic, Ewan ;
Gruau, Gerard ;
Durand, Patrick .
LANDSCAPE ECOLOGY, 2021, 36 (12) :3383-3399
[9]   Geomorphic thresholds in riverine landscapes [J].
Church, M .
FRESHWATER BIOLOGY, 2002, 47 (04) :541-557
[10]  
Curran-Cournane, 2015, INT J ENV ECOLOGICAL, V9, P227, DOI DOI 10.5281/ZENODO.1100402