Dominika Krol

Dr. Dominika Krol

orcid

Research Focus & Metrics

Academic Career Length

12Years (2015-Present)

(Calculated once Scilit publication data is synced: current year − year of first publication + 1)

Representative Publications

View All Publications
1 September 2016 in Science of The Total Environment
Verified
Journal Article
Closed access
Mary HartyMary Harty
Mary Harty
PFP.J. Forrestal
P.J. Forrestal
CWC.J. Watson
C.J. Watson
KMK.L. McGeough
K.L. McGeough
RCR. Carolan
R. Carolan
GLG.J. Lanigan
G.J. Lanigan

1 November 2019 in Journal of Cleaner Production
Verified
Journal Article
Closed access
IKI. Kavanagh
I. Kavanagh
WBW. Burchill
W. Burchill
MHMark Gerard Mark Gerard Healy
Mark Gerard Mark Gerard Healy
OFO. Fenton
O. Fenton
DKDominika Krol
Dominika Krol
GLG.J. Lanigan
G.J. Lanigan

1 October 2016 in Science of The Total Environment
Verified
Journal Article
Closed access
DKDominika Krol
Dominika Krol
RCR. Carolan
R. Carolan
EME. Minet
E. Minet
KMK.L. McGeough
K.L. McGeough
CWC.J. Watson
C.J. Watson
KRKarl G Richards
Karl G Richards

1 July 2020 in Science of The Total Environment
Verified
Journal Article
Closed access
DKDominika Krol
Dominika Krol
PFP.J. Forrestal
P.J. Forrestal
DWD. Wall
D. Wall
GLG.J. Lanigan
G.J. Lanigan
JSJ. Sanz-Gomez
J. Sanz-Gomez
KRKarl G Richards
Karl G Richards

1 October 2021 in Science of The Total Environment
Verified
Journal Article
Closed access
SCSaoirse Cummins
Saoirse Cummins
JFJohn A. Finn
John A. Finn
KRKarl G Richards
Karl G Richards
GLGary J. Lanigan
Gary J. Lanigan
GGGuylain Grange
Guylain Grange
DKDominika Krol
Dominika Krol

30 June 2021 in Journal of Environmental Quality
Verified
Journal Article
Open access
PDF file
TWTony Van Der Weerden
Tony Van Der Weerden
ANAlasdair Noble
Alasdair Noble
CKCecile A. M. de Klein
Cecile A. M. de Klein
NHNicholas J Hutchings
Nicholas J Hutchings
RTRachel E. Thorman
Rachel E. Thorman
GVGerard Velthof
Gerard Velthof
Manure application to land and deposition of urine and dung by grazing animals are major sources of ammonia (NH3) and nitrous oxide (N2O) emissions. Using data on NH3 and N2O emissions following land‐applied manures and excreta deposited during grazing, emission factors (EFs) disaggregated by climate zone were developed, and the effects of mitigation strategies were evaluated. The NH3 data represent emissions from cattle and swine manures in temperate wet climates, and the N2O data include cattle, sheep, and swine manure emissions in temperate wet/dry and tropical wet/dry climates. The NH3 EFs for broadcast cattle solid manure and slurry were 0.03 and 0.24 kg NH3–N kg–1 total N (TN), respectively, whereas the NH3 EF of broadcast swine slurry was 0.29. Emissions from both cattle and swine slurry were reduced between 46 and 62% with low‐emissions application methods. Land application of cattle and swine manure in wet climates had EFs of 0.005 and 0.011 kg N2O–N kg–1 TN, respectively, whereas in dry climates the EF for cattle manure was 0.0031. The N2O EFs for cattle urine and dung in wet climates were 0.0095 and 0.002 kg N2O–N kg–1 TN, respectively, which were three times greater than for dry climates. The N2O EFs for sheep urine and dung in wet climates were 0.0043 and 0.0005, respectively. The use of nitrification inhibitors reduced emissions in swine manure, cattle urine/dung, and sheep urine by 45–63%. These enhanced EFs can improve national inventories; however, more data from poorly represented regions (e.g., Asia, Africa, South America) are needed.