Assessing P fertiliser use in vegetable production: agronomic and environmental implications

Soil Research ◽  
2010 ◽  
Vol 48 (8) ◽  
pp. 674 ◽  
Author(s):  
K. Y. Chan ◽  
T. Wells ◽  
D. Fahey ◽  
S. M. Eldridge ◽  
C. G. Dorahy

Vegetable production is often located in the peri-urban areas close to large cities. In Sydney, Australia, excessive levels of phosphorus (P) have been reported in the soils, and vegetable farms have long been regarded as a potential source of the P that enters Sydney’s waterways. We report vegetable production under varying soil P conditions and the consequent changes in soil P, as well as water quality of runoff and leachate after growing 5 crops in a field trial where inputs in the form of garden organic compost were compared to current farmers’ practice. No difference in vegetable yield was observed between 100 and 400 mg/kg of soil Colwell P (0–0.10 m); therefore, our results indicate that the excessive soil P levels in the vegetable farms around Sydney are not important for optimal vegetable production. Results from runoff and leachate studies clearly demonstrate that high concentrations of P in soils used for vegetable production under the current farming practice around Sydney have increased the potential to export P and to negatively affect water quality of receiving environments. The significant increases in soluble P concentrations found in the soil and runoff water from the current farming practice can be attributed to the use of poultry litter. In contrast, using compost in place of poultry litter resulted in significantly reduced soil P accumulation and P concentration in runoff and leachate. Training and education programs for farmers and their advisors are recommended to encourage more sustainable fertiliser management practices and reduce the accumulation of P in the environment.

HortScience ◽  
1999 ◽  
Vol 34 (3) ◽  
pp. 465B-465 ◽  
Author(s):  
Warren Roberts ◽  
Jim Duthie ◽  
Jonathan Edelson ◽  
Jim Shrefler

Poultry litter is readily available in eastern Oklahoma. Poultry litter contains most of the essential elements for plant growth, and has long been used as a fertilizer for various crops. The ratio of N-P-K is about 1-1-1. In some areas, litter has been used excessively, and buildups of certain nutrients have occurred. There are concerns that a buildup of phosphorus (P) will lead to excessive amounts of P in water systems, which will affect water quality. There are also concerns that nitrogen (N) will leach or run off into water systems and also lower the water quality. Oklahoma has enacted legislation that will control how much litter can be applied to a given field, and regulations are being set in place to monitor and control the applications of litter. Studies have been conducted at the Lane Agricultural Center in southeastern Oklahoma over the past 6 years to determine vegetable production and soil nutrient changes when different litter application strategies are followed. In general, poultry litter has produced yields of cucumbers, collards, and corn that are equal to or greater than yields of the same crops fertilized with conventional synthetic fertilizers. Buildups of certain nutrients, particularly P, are occurring. At this time, the buildups are considered beneficial. The highest rate of litter application has resulted in levels of soil P that are about half the maximum amount allowed under present legislation.


2018 ◽  
Vol 13 (2) ◽  
pp. 42-54 ◽  
Author(s):  
Jarrett Okita ◽  
Cara Poor ◽  
Jessica M. Kleiss ◽  
Ted Eckmann

Green roofs have become a common method to increase water retention on-site in urban areas. However, the long-term water quality of runoff from green roofs is poorly understood. This study evaluated the water quality of stormwater runoff from a regular (non-vegetated) roof, a green roof installed 6 months previously, and a green roof installed 6 years ago in Portland, Oregon. Samples of runoff were taken during every rain event for 10 months, and analyzed for total phosphorus (TP), phosphate (PO3-4), total nitrogen (TN), nitrate (NO-3), ammonia (NH3), copper (Cu), and zinc (Zn). Runoff from the green roofs had higher concentrations of TP and PO3-4 and lower concentrations of Zn compared to the regular roof. Average TP concentrations from the 6-year old roof and 6-month old roof were 6.3 and 14.6 times higher, respectively, than concentrations from the regular roof, and average PO3-4 concentrations from the 6-year old roof and 6-month old roof were 13.5 and 26.6 times higher, respectively, compared to the regular roof. Runoff from the 6-month old green roof had higher concentrations of TP and PO3-4 than the 6-year old green roof during the wet season, but lower concentrations during the dry season. The 6-month old green roof installations where receiving waters are sensitive or impaired may need additional treatment methods to reduce phosphorus levels. As green roofs age, water retention decreases and phosphorus leaching increases during the dry season.


1979 ◽  
Vol 10 (2-3) ◽  
pp. 171-190
Author(s):  
Pertti Lahermo ◽  
Jouko Parviainen

In this study the changes in the quality of groundwater are described on the basis of material collected at some groundwater extraction plants situated mainly in urban areas. The causes of the marked increase in the content of dissolved solids are evaluated from the 1960s onwards.


2011 ◽  
Vol 91 (3) ◽  
pp. 329-338 ◽  
Author(s):  
Peter Kleinman ◽  
Andrew Sharpley ◽  
Anthony Buda ◽  
Richard McDowell ◽  
Arthur Allen

Kleinman, P. J. A., Sharpley, A. N., Budda, A. R., McDowell, R. W. and Allen, A. L. 2011. Soil controls of phosphorus in runoff: Management barriers and opportunities. Can. J. Soil Sci. 91: 329–338. The persistent problem of eutrophication, the biological enrichment of surface waters, has produced a vast literature on soil phosphorus (P) effects on runoff water quality. This paper considers the mechanisms controlling soil P transfers from agricultural soils to runoff waters, and the management of these transfers. Historical emphases on soil conservation and control of sediment delivery to surface waters have demonstrated that comprehensive strategies to mitigate sediment-bound P transfer can produce long-term water quality improvements at a watershed scale. Less responsive are dissolved P releases from soils that have historically received P applications in excess of crop requirements. While halting further P applications to such soils may prevent dissolved P losses from growing, the desorption of P from soils that is derived from historical inputs, termed here as “legacy P”, can persist for long periods of time. Articulating the role of legacy P in delaying the response of watersheds to remedial programs requires more work, delivering the difficult message that yesterday's sinks of P may be today's sources. Even legacy sources of P that occur in low concentration relative to agronomic requirement can support significant loads of P in runoff under the right hydrologic conditions. Strategies that take advantage of the capacity of soils to buffer dissolved P losses, such as periodic tillage to diminish severe vertical stratification of P in no-till soils, offer short-term solutions to mitigating P losses. In some cases, more aggressive strategies are required to mitigate both short-term and legacy P losses.


Author(s):  
Sajjad Haydar ◽  
Obaidullah Nadeem ◽  
Ghulam Hussain ◽  
Haroon Rashid ◽  
Rashid Majeed

A study was conducted to evaluate the drinking water quality of Gujranwala city. Samples were collected from 16 locations including: 4 tube wells, 4 overhead reservoirs (OHR) and 8 house connections. Twelve physicochemical and two bacteriological parameters were tested, before and after monsoon and compared with National Standards for Drinking Water Quality (NSDWQ). The results demonstrated that most of the physicochemical parameters, except lead, nickle and chromium were within NSDWQ before and after monsoon. Bacteriological and heavy metal contamination was found before and after the monsoon. Possible reasons of contamination are: no disinfection, old and leaking water pipes, poor drainage duringmonsoon and possible cross connections between water and sewerage lines. It is recommended to practice disinfection, laying of water and sewerage pipes on opposite sides of streets and periodic water quality monitoring.


2021 ◽  
Author(s):  
Genda Singh ◽  
P.R. Nagora ◽  
Parul Haksar ◽  
Deepak Mishra

Abstract This study aimed at analysing water quality of effluent-dominated seasonal rivers and its impacts on soil and vegetation. Effluent-inflicted, river-edge and non-polluted areas were selected at 5 places along Luni, Bandi and Jojari rivers in western Rajasthan. Water of rivers exhibited high pH (7.6-8.6), electrical conductivity (EC 2.45-38.3 dSm-1), total dissolved and suspended solids, alkalinity and Na (1.50-30.00 gL-1), K, Ca and Mn (25.2-2439.3 µgL-1) concentrations and low NH4-N (1.08-20.69 mgL-1), NO3-N (0.44-9.10 mgL-1) and PO4-P (3.10-13.40 mgL-1). Most variables were highest for Luni and lowest for Bandi River. Cu, Co, Se, Cd and Pb concentrations were <180 µgL-1. Soil pH, EC and PO4-P were highest along Bandi, whereas NH4-N, NO3-N and K were highest along Jojari River in both 0-30 and 30-60 cm soil layers. Effluent-inflicted soils exhibited high pH, EC and PO4-P, whereas non-polluted soils showed high NH4-N, NO3-N and K availability. These soil variables decreased downstream. Plant species number ranged between 34 along Luni and 20 along Jojari (total 10 trees, 10 shrubs and 29 herbaceous). Species richness (R) and diversity (H’) of trees were highest along Bandi. Shrubs and herbaceous R, H’ and evenness (e’) were high along Luni. Least diverse vegetation was along Jojari. Non-polluted area exhibited high tree R and H’, whereas river-edge showed high herbaceous R and H’. Effluent-inflicted area showed high salts and low diversity, but dominated by Aeluropus lagopoides, Paspalum virgatum, Phragmites karka, Tamarix ericoides, etc., which can be used in restoring such degraded urban areas.


2021 ◽  
Vol 61 (7) ◽  
pp. 637
Author(s):  
Louise Edwards ◽  
Helen Crabb

Context Water is the first nutrient and an essential component of all agricultural production systems. Despite its importance there has been limited research on water, and in particular, the impact of its availability, management and quality on production systems. Aims This research sought to describe the management and quality of water used within the Australian pig industry. Specifically, the water sources utilised, how water was managed and to evaluate water quality at both the source and the point of delivery to the pig. Methods Fifty-seven commercial piggeries across Australia participated in this study by completing a written survey on water management. In addition, survey participants undertook physical farm parameter measurements including collecting water samples. Each water sample was tested for standard quality parameters including pH, hardness, heavy metals and microbiological status. Key results Responses were received from 57 farms, estimated to represent at least 22% of ‘large’ pig herds. Bore water was the most common water source being utilised within the farms surveyed. Management practices and infrastructure delivering water from the source to the point of consumption were found to differ across the farms surveyed. Furthermore, water was regularly used as a delivery mechanism for soluble additives such as antibiotics. The quality of water at the source and point of consumption was found to be highly variable with many parameters, particularly pH, hardness, salinity, iron, manganese and microbiological levels, exceeding the acceptable standard. Conclusions In general, water quality did not appear to be routinely monitored or managed. As a result, farm managers had poor visibility of the potential negative impacts that inferior water quality or management may be having on pig production and in turn the economics of their business. Indeed, inferior water quality may impact the delivery of antibiotics and in turn undermine the industry’s antimicrobial stewardship efforts. Implications The study findings suggest that water quality represents a significant challenge to the Australian pig industry. Access to drinking water of an acceptable quality is essential for optimal pig performance, health and welfare but also to ensure farm to fork supply chain integrity, traceability and food safety.


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